CCQM-K55.b Final Report October 2012 Page 1 of 41
CCQM-K55.b (Aldrin)
Final Report: October 2012
CCQM-K55.b Key Comparison on the
Characterization of Organic Substances for Chemical Purity
Coordinating laboratory:
Steven Westwood*, Ralf Josephs, Tiphaine Choteau, Adeline Daireaux, Charline Mesquida and Robert Wielgosz
Bureau International des Poids et Mesures (BIPM, Coordinating laboratory)
Sèvres, France

With contributions from:
Adriana Rosso and Mariana Ruiz de Arechavaleta
Instituto Nacional de Tecnologia Industrial (INTI)
Buenos Aires, Argentina

Stephen Davies and Hongjie Wang
National Measurement Institute (Australia) (NMIA)
Pymble, NSW, Australia

Eliane Cristina Pires do Rego, Janaína Marques Rodrigues, Evelyn de Freitas Guimarães, Marcus Vinicius Barreto
Sousa, Tânia Maria Monteiro, Laura Alves das Neves Valente, Fernando Gustavo Marques Violante, Renato Rubim
Ribeiro Almeida, Maria Cristina Baptista Quaresma and Raquel Nogueira
Instituto Nacional de Metrologia, Qualidade e Tecnologia (INMETRO)
Xerem, Brazil

Anthony Windust
Institute for National Measurement Standards - National Research Council Canada (NRC-INMS)
Ottawa, Canada

Xinhua Dai, Xiaomin Li, Wei Zhang, Ming Li, Mingwu Shao, Chao Wei
National Institute of Metrology (China) (NIM)
Beijing, China

Siu-kay Wong
Government Laboratory of Hong Kong SAR (GLHK)
Kowloon, Hong Kong SAR

Julie Cabillic, Fanny Gantois
Laboratoire National de Métrologie et d’Essais (LNE)
Paris, France

Rosemarie Philipp, Dietmar Pfeifer, Sebastian Hein, Urszula-Anna Klyk-Seitz
Bundesanstalt für Materialforschung (BAM)
Berlin, Germany

Keiichiro Ishikawa
National Metrology Institute of Japan (NMIJ)
Tsukuba, Japan

CCQM-K55.b Final Report October 2012 Page 2 of 41
Esther Castro and Norma Gonzalez
Centro Nacional de Metrologia (CENAM)
Querétaro, Mexico

Anatoly Krylov
D.I. Mendeleyev Scientific and Research Institute for Metrology (VNIIM)
St Petersburg, Russia

Teo Tang Lin and Lee Tong Kooi
Health Sciences Authority (HSA)
Singapore

M. Fernandes-Whaley, D. Prévoo, M. Archer,R. Visser, N. Nlhapo and B. de Vos
National Metrology Institute of South Africa (NMISA)
Pretoria, South Africa

Seonghee Ahn
Korea Research Institute of Standards and Science (KRISS)
Daejeon, South Korea

Preeyaporn Pookrod, Kanjana Wiangnon, Nittaya Sudsiri, Kittiya Muaksang and Chainarong Cherdchu
National Institute of Metrology (Thailand) (NIMT)
Bangkok, Thailand

Ahmet Ceyhan Gören and Mine Bilsel
National Metrology Institute of Turkey (UME)
Gebze-Kocaeli, Turkey

Thierry LeGoff
LGC Limited (LGC)
Teddington, United Kingdom

Dan Bearden, Mary Bedner, David Duewer, Diane Hancock, Brian Lang, Katrice Lippa, Michele Schantz
and John Sieber
National Institute of Standards and Technology (NIST)
Gaithersburg, MD, USA

Comparison coordinator: Steven Westwood, BIPM (steven.westwood@bipm.org)

CCQM-K55.b Final Report October 2012 Page 3 of 41
Introduction
The CCQM-K55 comparison was undertaken by the CCQM Organic Analysis Working Group (OAWG)
for National Measurement Institutes (NMIs) and Designated Institutes (DIs) which provide measurement
services in organic analysis under the CIPM Mutual Recognition Arrangement (MRA). The ability to
perform suitable purity assessment on the materials that an NMI either makes available to external users
as pure substance reference materials or that are used by an NMI as their primary calibrators for the
assignment of the property values either of solution or matrix reference materials or for their reference
measurement services is a core technical competency for the provision of measurement results in organic
analysis that are traceable to the SI. The purity property value (generally reported for applications in
organic analysis as the mass fractiona of the main component) assigned to the primary calibrator in a
measurement hierarchy underpins the traceability chain for all results linked to that calibrator. All NMIs
with ongoing programs in organic analysis were encouraged to participate in this series of comparisons.
The comparisons allow NMIs and DIs to demonstrate that their procedure(s) for assignment of a purity
property value and its associated uncertainty are fit for purpose for their intended application(s).
Summary of Previous Studies
The CCQM-P20 multi-round pilot study on purity determination was completed prior to the CCQM-K55
comparison. Studies were undertaken on the purity assessment of tributyl tin chloride (CCQM-P20.a),
xylene (CCQM-P20.b), atrazine (CCQM-P20.c), chlorpyrifos (CCQM-P20.d), theophylline
(CCQM-P20.e)1 and digoxin (CCQM-P20.f)2.
The “mass balance” or “summation of impurities” method for purity assessment, which aims to identify
and quantify on a mass fraction (mg/g) basis all the orthogonal classes of impurity present in the material
and by subtraction provides a measure of the mass fraction of the main component, was the most widely
used approach by participants in the CCQM-P20 pilot studies. However the use of quantitative nuclear
magnetic resonance (qNMR) approaches to obtain a direct measure of the content of the main component
were also increasingly being used.
The BIPM coordinated the final two rounds of the CCQM-P20 pilot study and developed a “molecular
weight v. polarity” model to map the analytical space for comparisons in this area. This model provided
the criteria for the selection of the measurands for each of the four consecutive rounds – respectively
CCQM-K55.a, CCQM-K55.b, CCQM-K55.c and CCQM-K55.d – that make up the initial CCQM-K55
key comparison. The relation based on this model between the proposed CCQM-K55 comparison
materials, potential future measurands and major areas of calibration and measurement capability (CMC)
claims for the provision of primary calibrators and calibration solutions for organic analysis currently
accepted or under consideration under the CIPM Mutual Recognition Arrangement is shown in Annex A.
The OAWG meeting at Sèvres in April 2008 accepted this overall strategy for the comparison as well as
the specific measurand, 17β-estradiol, proposed for the first comparison round, CCQM-K55.a. A pilot
study, CCQM-P117.a, was undertaken in parallel with the key comparison. The CCQM-K55.a comparison
was completed in 2009 and the Final Report was published in September 2012 in Appendix B of the
BIPM Key Comparison Database.3
The BIPM proposed aldrin as the measurand for CCQM-K55.b. The proposal was discussed at several
OAWG meetings and approved at the April 2009 meeting at Sèvres. The comparison samples were
distributed in May 2010. The individual results were communicated to the comparison coordinator in
August 2010 and the results were first discussed at the November 2010 meeting of the CCQM OAWG in

a For the purposes of this comparison, the mass fraction of both the main component and associated impurities are expressed in
units of mg/g. The upper limit value of 1000 mg/g would correspond to a “100 %” pure material.

CCQM-K55.b Final Report October 2012 Page 4 of 41
Singapore. Further studies were subsequently undertaken to resolve a disparity between the results
obtained by mass balance approaches and those obtained by qNMR. This difference, which was finally
ascribed to the presence of a significant non-volatile organic impurity (ca. 1% on a relative mass fraction
basis) which was not detected by the majority of participants was further discussed at the April 2011
OAWG meeting at Sèvres and an assignment of a KCRV proposal for aldrin in CCQM-K55.b based on
combination of separate KCRV estimates for contributing orthogonal impurity classes was accepted.
Aldrin
Aldrin was selected as the measurand for the second round of the comparison because it:
 provides an analytical challenge representative of a laboratory’s capability for the purity assignment
of organic compounds of medium structural complexity and low polarity (see “How Far The Light
Shines” statement);
 represents a sector for general CMC claims on the “analysis space” model (Annex A) which is
distinct from the area already covered by the CCQM-K55.a measurand, estradiol.
 is a chlorinated pesticide for which there are a number of specific CMC claims in Appendix C of the
BIPM Key Comparison Database;
 is classified as a Persistent Organic Pollutant (POP) and an important analyte in its own right in the
areas of environmental and food residue analysis
 is safe and stable for transport in the amounts involved for the comparison and was available in
sufficient amount to allow the preparation of a relatively large batch of the comparison sample.
The structure of aldrin (1) is shown in Figure 1 with the conventional ring numbering in bold. The
structure of other compounds related to aldrin and referred to in this report are given in Annex B.

Cl Cl
Cl
Cl
Cl
Cl
H
H
H
H
H
H
HH
1
2
3
4
5
6
7
8
9
10
11
12a12s

Figure 1 – Structure and ring-numbering of Aldrin
Pure aldrin is a colourless solid with a reported melting point of 104 °C. It is insoluble in water,
moderately soluble in alcohols and generally soluble in non-polar organic solvents. CMC claims for the
measurement of aldrin, disseminated as both pure substance and standard solution CRMs, are listed in the
BIPM Key Comparison Database (KCDB) Appendix C.

CCQM-K55.b Final Report October 2012 Page 5 of 41
KEY COMPARISON – MATERIAL AND CONDUCT OF STUDY
For the preparation of the study material for the CCQM-K55.b comparison and the parallel pilot study
CCQM-P117.b, a bulk sample of technical grade aldrin donated by the NMIA was used as the source
material. This material was a dark, aggregated solid. It contained less than 90% aldrin as determined by
relative GC-FID response. A number of related structure or residual starting material impurities were
present at significant levels in the material and which were identified by GC-MS.
Trial purification of the material by recrystallisation was investigated using various organic solvent
combinations. The most suitable solvent for scaling up the production of the source material was
determined to be aqueous methanol. Three successive recrystallisations, which included some
recombination of crops obtained from earlier recrystallisation rounds, were required to produce a bulk
material having aldrin content greater than 95% by relative GC-FID response.
This material was dried under vacuum at room temperature, ground in a planetary ball mill to give a free
running grey powder and redried to constant weight under vacuum at 40 °C.
The ground, dried bulk material was subdivided into a batch of 150 individual units given the BIPM
identifier OGP.014. Each unit of BIPM OGP.014 contained a minimum of 500 mg of aldrin in a glass
storage vial (5 mL capacity) fitted with a rubber insert and crimped with an aluminium cap.
The batch of candidate material vials were evaluated for impurity profile, homogeneity and stability at the
BIPM. The mass fraction of aldrin in the comparison material was assessed by the BIPM to be greater
than 950 mg/g while the homogeneity and stability of the aldrin and the associated impurity components
were suitable for the purposes of the comparison.
A summary of the results for aldrin content and for characterization of the material’s impurity profile
reported by the study participants are contained in this report.
“How Far The Light Shines” Statement for CCQM-K55.b
The comparison is intended to demonstrate a laboratory’s performance in determining the mass fraction of
the main component in a relatively pure organic material. The measurement results should be indicative of
the performance of a laboratory’s measurement capability for the purity assignment of organic compounds
of medium structural complexity (relative molecular mass range 300-500) and low polarity (pKOW < -2)
where KOW is the octanol-water partition coefficient
4 and is representative of compounds for which related
structure impurities are generally quantified by capillary gas-phase chromatography.
The expected overall outcome of the rounds making up the CCQM-K55 comparison is to evaluate through
a series of strategically planned exercises the scope, applicability, limitations and appropriateness of the
various procedures used to assign mass fraction property values to organic materials.

CCQM-K55.b Final Report October 2012 Page 6 of 41
Characterisation study
The methods used to investigate, assign and confirm the quantitative composition of the CCQM-K55.b
candidate material by the BIPM are summarised below.
Characterization studies
Related structure impurity content was evaluated by:
a. GC-FID
b. GC-MS
c. LC-UV
d. 1H and 13C NMR
Water content was evaluated by:
a. coulometric Karl Fischer titration with oven transfer of water from the sample
b. coulometric Karl Fischer titration using direct addition of the sample
c. thermogravimetric analysis (TGA) as a consistency check for the assigned value
d. microanalysis (% C,H content) as a consistency check for assigned value
Residual solvent content was evaluated by:
a. GC-MS by direct injection
b. Headspace GC-MS
c. 1H NMR
d. Thermogravimetric analysis as a consistency check for the assigned value
e. Microanalysis (% C,H content) as a consistency check for the assigned value
Non-volatile/ inorganics content :
a. ICP-MS for common elements (Na, K, Ca, Mg, Si, Fe, Al)
b. Microanalysis (% C, H content) as a consistency check for the assigned values
Main component (Aldrin) content
a. qNMR
b. Differential scanning calorimetry (DSC)
Homogeneity studies
i. Related structure components
The homogeneity of minor components related in structure to aldrin were assessed by sampling ten
sub-units selected from across the candidate material batch with analysis by GC-FID and
separately by LC-UV with detection at 220 nm. The minimum sample size used to prepare each
analysis sample was 2.5 mg.
ii. Water
The homogeneity of the material relative to water content was assessed by coulometric Karl
Fischer titration using oven transfer and a minimum sample size of 50 mg per analysis on five sub-
units representative of the candidate material batch
iii. Residual solvent
The homogeneity of the material relative to methanol content was assessed by direct injection GC-
MS analysis using a minimum sample size of 10 mg per analysis on five sub-units representative
of the candidate material batch.

CCQM-K55.b Final Report October 2012 Page 7 of 41
iv. Inorganics content
Three units selected from across the production batch were analysed by ICP-MS and by elemental
microanalysis for carbon and hydrogen. All gave metal content levels below the detection limits
(25 ppm) for each element. Results for % C, H content were in accord with the molecular formula
of aldrin
v. Aldrin
As a consistency check, the homogeneity of the aldrin content in the material was assessed using
the ten sub-units selected for the related structure impurity study by the same GC-FID and LC-UV
methods developed for the related structure impurity characterisation. In addition a limited qNMR
study was undertaken (two samples from two units of CCQM-K55.b), using dimethyl terephthalate
as the internal standard, which gave a value of 958 mg/g with standard uncertainty 2 mg/g for the
aldrin content of the sample
The uncertainty contributions due to the inhomogeneity of each related structure impurity component were
evaluated by ANOVA. This provided an estimate of the variation due to inhomogeneity of each impurity
at a stated sampling size both between and within sample units.
The uncertainty contributions due to the inhomogeneity of the major related structure components
detected by GC-FID (ubb(rel)) were evaluated by ANOVA. This provided an estimate of the variation due to
inhomogeneity of related structure impurities at the stated sampling size both between and within sample
units. Acceptable uncertainty contributions due to inhomogeneity were observed for each of the resolved
impurities present in the sample. Table 1 shows the estimated content, ubb(rel) and ubb(abs) for each of the
resolved related sttructure impurities, and a combined value for the overall uncertainty contribution from
between unit inhomogeneity (ubb) of the related structure impurities content of the material. This was
calculated as 0.42 mg/g by quadratic combination of the absolute inhomogeneity uncertainties for each
impurity.

Impurity Content (mg/g) from
homogeneity study*
ubb(rel) (%) ubb(abs) (mg/g)
Isodrin 27 1.36 0.37
Dieldrin 3.0 1.08 0.03
Dechlorane 4.0 5.0 0.20
Minor impurities 1.5 2.0 0.03
Combined related
structure impurities
35.5 1.2 0.42
* From relative GC-FID peak area – uncorrected for differential response factors or other impurities
Table 1: Homogeneity assessment for related structure impurities in CCQM-K55.b
Karl Fischer titration was used to assess variations in water content of the material. As the level of water
in the material was below the limit of quantification of our method, it was not possible to estimate the
uncertainty of between unit inhomogeneity of the water content of the material in a rigorous manner.
There was however no evidence of significant inter-sample differences.

CCQM-K55.b Final Report October 2012 Page 8 of 41
The contribution to the overall uncertainty from between unit inhomogeneity of the methanol content of the
material was estimated at ubb(MeOH) = 0.1 mg/g from comparison of the within unit and between unit
repeatability of the analysis of two 10 mg replicates taken from each of five units of the candidate material.
The within unit repeatability (sr) under these conditions was 0.1 mg/g.
Stability studies
An isochronous stability study was performed using a reference storage temperature of -20 °C and test
temperatures of 4°C, 22 °C and 40 °C. A set of units from the production batch were stored at each
selected temperature over 8 weeks, with units transferred to reference temperature storage at 2-week
intervals.
Trend analysis of the data obtained by GC-FID analysis of the stability test samples under repeatability
conditions indicated no significant change in the relative composition of aldrin or of the related structure
components over this time at any of the test temperatures.
No significant changes in water content, which in any case were all below the level of quantification of
our method, were observed after storage at 4 °C or 22 °C. There was some evidence of minor uptake of
water but only after prolonged storage at 40 °C. The methanol content of the material was stable on
storage at 4 °C and 22 °C but did decrease significantly after storage beyond 6 weeks at 22 °C or 2 weeks
at 40 °C.
The effect of storage temperature on methanol content of the comparison material is shown in Figure 2.

MeOH in CCQM-K55.b: Temperature Stability
1.5
2.0
2.5
3.0
0 2 4 6 8
Time (weeks)
M
eO
H
co
nt
en
t (
m
g/
g)
4 C
22 C
40 C

Figure 2 Effect of storage temperature on methanol content of comparison material

CCQM-K55.b Final Report October 2012 Page 9 of 41
On the basis of these studies it was concluded that for the purposes of the comparison the material was
suitably stable for short-term transport at ambient temperature, provided it was not exposed to
temperatures significantly in excess of 40 °C, and for longer term storage at 4 °C.
To minimise the potential for changes in the material composition due to loss of methanol, participants
were instructed to store the material at 4 °C.
Sample distribution
Two units of the study sample, each containing a minimum of 500 mg of material, were distributed to
each participant. Participants were asked to return a form acknowledging receipt of the samples and to
advise the co-ordinator if any obvious damage had occurred to the vials during shipping. Recipients were
asked to confirm that a monitoring strip inside the shipping container had not registered a temperature in
excess of 37 °C during the transport process.
The monitor strips indicated that the units originally supplied to Singapore (HSA) were exposed to
temperatures in excess of 40 °C during shipping. A replacement set was provided in this case which was
delivered without incident. There was also a prolonged delay in delivery of the original sample sent to
CENAM due to customs clearance problems. A replacement sample set was issued, which was delivered
without difficulties. Otherwise all samples were delivered to the comparison participants without incident.
Every registered participant in the CCQM-K55.b comparison provided a result for their sample.
Quantities and Units
Participants were required to report the mass fraction of aldrin, the major component of the comparison
sample, in one of the two units supplied to them. The additional unit was provided for method
development and trial studies.
In addition all participants who used a mass balance (summation of impurities) procedure to determine the
aldrin content were required to report the combined mass fraction assignment and associated uncertainty
for some or all of the following sub-classes of impurity.

i. total related structure organic substances
ii. water
iii. total residual organic solvent / volatile organic compounds (VOCs)
iv. total non-volatile organics & inorganics

Participants were encouraged to also provide mass fraction estimates for the main impurity components
they identified in the comparison sample.

CCQM-K55.b Final Report October 2012 Page 10 of 41
Reported Mass Fraction of Aldrin in CCQM-K55.b
The values reported by participants for aldrin content in CCQM-K55.b are given in Table 2 with a
summary plot in Figure 3.
Participant Aldrin
(mg/g)
Standard
Uncertainty (mg/g)
Coverage
factor
Expanded
Uncertainty (mg/g)
NRC-INMS 947.8 3.0 2 6.1
NMIJ 950.1 3.23 2 6.5
HSA 950.4 1.3 2 2.6
BAM 953 4 2 8.0
NIMT 958.5 1.4 2 2.8
NMISA 960.2 1.9 2 3.7
CENAM * 960.7 3.5 2 7.0
LGC 960.9 1.9 2 3.8
NIST 961 NA NA +1.6 / -1.8
KRISS 961.6 0.9 2 1.8
UME 961.7 1.0 2 2.1
LNE 962.0 0.47 2 0.93
NMIA 962.1 2.4 2.07 4.9
BIPM 962.6 +0.65 / -0.75 2 +1.3 / -1.5
GLHK 963.1 1.7 2 3.4
INTI 963.7 9.5 2 19
NIM 964.6 1.2 2 2.4
INMETRO 966.8 0.57 2.45 1.4
VNIIM 972.6 0.9 2 1.8
Table 2 : Aldrin content for participants in CCQM-K55.b
* Revised value from initially reported result, received prior to circulation of all results

CCQM-K55.b Final Report October 2012 Page 11 of 41
Aldrin content in CCQM-K55.b
940
950
960
970
980
990
1000
IN
M
S
-N
R
C
N
M
IJ
H
S
A
B
A
M
N
IM
T
N
M
IS
A
C
E
N
A
M
*
L
G
C
N
IS
T
K
R
IS
S
U
M
E
L
N
E
N
M
IA
B
IP
M
G
L
H
K
S
A
R
IN
T
I
N
IM
IN
M
E
T
R
O
V
N
IIM
A
ld
ri
n
(
m
g
/g
)

Figure 3 Aldrin content reported by participants in CCQM-K55.b
(plotted with 95% confidence interval expanded uncertainties)
* Revision of initially reported result, received prior to the circulation of all results
Disparity between Mass Balance and qNMR estimates for Aldrin in CCQM-K55.b
Inspection of the reported values for aldrin content in CCQM-K55.b shows that the comparison results can
be divided into two main groups – one having a consensus value for aldrin in excess of 960 mg/g and a
second where the assigned value is in the vicinity of 950 mg/g.
The higher estimate was obtained by participants using a mass balance approach in which hyphenated
chromatography - and qNMR in the case of NIST - was used to determine the total related structure
impurity levels with contributions from other potential classes of impurities obtained by complimentary
techniques. The aldrin content of CCQM-K55.b was then assigned by subtraction of the combined
impurity estimate from the theoretical maximum of 1000 mg/g.
The group of results with the lower assigned value for aldrin were based on qNMR techniques to directly
determine the aldrin content either as the stand-alone approach or undertaken in conjunction with a mass
balance approach.

CCQM-K55.b Final Report October 2012 Page 12 of 41
The direct assignment of aldrin content by qNMR was achieved by integration of the signal due to the
equivalent olefinic H4- and H5-protons (Fig. 1), which are distinct from interfering signals due to the
main impurities - isodrin, dieldrin, dechlorane and methanol. Representative 1H NMR spectra for CCQM-
K55.b including an expansion of the main region containing signals due to the various impurities are
reproduced in Annex C.
The NMIJ and the HSA were the only participants to report a mass balance assignment below 955 mg/g.
In each case they obtained direct qNMR values for aldrin in the vicinity of 950 mg /g. Their mass balance
estimates were in agreement within their stated uncertainties with this value, and were markedly lower
than those reported by other participants, because they reported a significant level (ca. 10 mg/g) for non-
volatile organic impurity, which was not identified by other participants. It should be noted that the NRC-
INMS in CCQM-K55.b and the SIRIM, who participated in the parallel CCQM-P117.b pilot study, both
using qNMR as a stand alone technique, also assigned the aldrin content at a level consistent with those
reported by the NMIJ and HSA.
The situation however was not simply a choice between a low qNMR estimate and (generally) a higher
mass balance value for aldrin. The NMIA, BIPM and UME all obtained qNMR assignments for aldrin
content that were in excess of 955 mg/g and were consistent within their associated expanded uncertainty
estimates with their independent mass balance values.
A combined comparison plot of aldrin content obtained by participants by direct qNMR compared with
the mass balance value obtained by the same participant is shown in Figure 4. In several cases the qNMR
data shown in Figure 4 was not included in the participant’s report but was made available to the study
coordinator subsequent to the circulation of the comparison results and the initial discussion at the
November 2010 OAWG meeting. The additional information on qNMR conditions and results, with
comparison with the mass balance value reported where available, are summarised in Table 3.
Note that in Figure 4 results are plotted with their standard uncertainties or the standard deviation of the
qNMR estimate rather than the expanded uncertainties as shown in other data graphs.



Figure 4 Comparison of direct qNMR and mass balance values (± uc or std. devn.) provided by the
same participant for aldrin content of CCQM-K55.b (*CCQM-P117.b for SIRIM).

CCQM-K55.b Final Report October 2012 Page 13 of 41

Participant Solvent(s) Quantification
Standard
Aldrin (mg/g) by
“direct” qNMR
Aldrin (mg/g) by
“mass balance”
BAM CDCl3 Benzoic acid 944.6 961.4
LGC CDCl3 Trioxane 947 (σ = 2.6) 960.9 (uc = 1.9)
NRC-INMS CDCl3, CD3OD Benzoic acid 947.8 (uc = 3)
INMETRO CDCl3 Benzoic acid 948.5 (σ = 2.1) 966.8 (uc = 0.6)
NIST CD3OD Benzoic acid 949 (uc = 0.7) 961 (uc = 0.8)
NMIJ CD2Cl2 Benzoic acid 952.9 (uc = 2.9) 947.2 (uc = 1.1)
UME d6-Acetone 1,4-DCB 957.4 (uc = 0.2) 961.7 (uc = 1.1)
BIPM d6-DMSO DMTP 958 (σ = 2) 962.6 (uc = 0.7)
NMIA d6-DMSO,
CD3OD, CDCl3
DMTP 963 (σ = 1.9) 962.1 (uc = 2.4)
HSA CDCl3 Benzoic acid 950 950.4 (uc = 1.3)
NIM CDCl3 Benzoic acid 946 (uc = 3.5) 964.7 (uc = 1.2)
SIRIM* CDCl3 Chlorpyrifos 950.1 (σ = 6.9)
Table 3 – qNMR and mass balance estimates for aldrin in CCQM-K55.b
(1,4-DCB = 1,4-Dichlorobenzene ; DMTP = Dimethyl terephthalate)
At the OAWG discussions in November 2010, the NMIJ presented supporting data from a GC-FID
external calibration using a certified sample of aldrin as the primary calibrant. Their value for aldrin
in CCQM-K55.b obtained in this manner was consistent with their reported value for the
comparison.
There was considerable discussion on possible reasons for the discrepancy between mass balance
and qNMR results at the November 2010 OAWG meeting. To attempt to resolve the issue additional
studies were requested in the following areas:
 homogeneity of aldrin in CCQM-K55.b by qNMR
 influence of solvent and internal standard on qNMR result for aldrin in CCQM-K55.b
 additional evidence for the presence of a significant non-volatile organic impurity
At the April 2011 OAWG meeting the results of qNMR studies on five samples of CCQM-K55.b
selected from across the production batch and undertaken by the NRC-INMS were reported. They
prepared triplicate samples from each unit and determined the aldrin content of solutions in CD3OD
with benzoic acid as the internal quantification standard. The results obtained, which also include
estimates for the associated impurities isodrin and methanol, are summarised in Table 4 and are
consistent with an aldrin content of CCQM-K55.b of 950 mg/g with no evidence of significant
inhomogeneity between the individual units. In addition, no effect on qNMR values due to use of
different solvent (comparing CD3OD with d6-DMSO) or internal standard (benzoic acid v. dimethyl
terephthalate) was found.

CCQM-K55.b Final Report October 2012 Page 14 of 41

Bottle Aldrin Isodrin MeOH
003-A 950.5 25.5 2.2
003-B 948.0 26.3 2.1
003-C 951.6 26.4 2.0
030-A 953.0 26.5 2.0
030-B 948.2 25.5 1.9
030-C 951.9 26.3 2.1
059-A 951.9 26.8 2.0
059-B - - -
059-C 952.5 26.4 2.3
090-A 952.0 26.5 1.8
090-B 951.7 26.4 1.9
090-C 946.9 25.2 2.1
125-A 952.2 26.6 2.0
125-B 952.8 26.5 2.0
125-C 945.4 25.9 2.2

Mean 950.6 26.2 2.0
sd 2.5 0.48 0.1
rsd 0.3% 1.8% 5%
Table 4 – qNMR results (mg/g) for homogeneity check of aldrin, isodrin and methanol in CCQM-K55.b
(data provided by NRC-INMS for solutions in CDCl3 using benzoic acid as quantification standard)
The NMIJ reported size-exclusion chromatography studies that indicated the presence of high molecular
weight impurities equivalent to approximately 1.2% of the peak area response by refractive index
detection relative to the response of the aldrin component. Peaks due to higher molecular weight species
were not observed when higher purity reference standards of aldrin were analysed under the same
conditions. A representative chromatogram is shown in Figure 5.











0 5 10 15min
AldrinDechlorane
“Polymer”
MW: 1000-2600
R
Ｉ
UV-VIS (400 nm)
Figure 5
Gel permeation chromatogram of
CCQM-K55.b (SHODEX KF-
401HQ column), elution with 100%
THF; detection by refractive index
(black) and UV (blue) response.
- reproduced from data provided by
the NMIJ

CCQM-K55.b Final Report October 2012 Page 15 of 41
The NMIJ also reported that cycles of dissolution and selective precipitation could be used to furnish
purified samples of the non-volatile impurity.
After consideration of the additional data the study participants agreed that the presence of a non-volatile
organic impurity that was not detected by the majority of mass balance approaches had been established
and that this resolved the apparent difference between the aldrin values assigned by the two approaches.
The cases where higher values for aldrin were originally obtained by qNMR were explained as arising
from software processing issues – in particular the applicability or otherwise of automated baseline
correction algorithms commonly used in processing the raw FID data. The NMIA reported that when they
used the automatic baseline correction option with their software they obtained a value for aldrin above
960 mg/g, but when this option was not used the result was 948 mg/g.
No further information is currently available as to the nature and structure of the impurity. Despite being
present at appreciable levels it has still not been observed directly by MS or NMR methods and did not
perturb the elemental analysis data for CCQM-K55.b significantly. This indicates that it is likely to be a
polychlorinated compound structurally related to aldrin or its synthetic precursors. One suggested
possibility is a mixture of oligo- or poly-(hexachlorocyclopentadiene), potentially formed as a side-
product of technical grade aldrin synthesis from hexachlorocyclopentadiene monomer.
Impurity Profile and Key Comparison Reference Values (KCRVs) for Impurity
Classes in CCQM-K55.b
All participants in CCQM-K55.b using a mass balance procedure to assign the aldrin content were
required to give estimates for the mass fraction of the sub-classes of impurities they quantified to obtain
their final aldrin mass fraction estimate. At the April 2011 WG meeting it was agreed that, as was done for
CCQM-P20.f and CCQM-K55.a, the comparison coordinator would propose an overall KCRV for the
aldrin content of CCQM-K55.b based on the combination of individual KCRVs for the mass fraction of
each of the orthogonal classes of impurity in the CCQM-K55.b comparison sample.
This required the assignment of separate KCRVs for:
 structurally related impurities;
 water;
 volatile organic solvent;
 non-volatiles/inorganics.

i. KCRV for Aldrin-related impurity content
The structures of the individual impurities reported by two or more participants are shown, with their
associated numbering, in Annex B. The major compounds identified by participants as present at levels
above 0.1 mg/g in CCQM-K55.b were, in decreasing order of mass fraction, isodrin (2), dieldrin (3),
dechlorane (4), dihydroaldrin (5) and endrin ketone (6). The detection in the sample at low levels (all
below 0.1 mg/g) of hexachlorocyclopentadiene (7), octachlorocyclopentene (8) and chlordene (9) was also
noted by several participants.
A GC-FID chromatogram obtained by NIST using a polar RTX-OP column was highly representative of
GC chromatograms obtained by all other participants and shows the relative retention time of each of the
main related structure impurities reported by participants and their structural assignment. It is reproduced

CCQM-K55.b Final Report October 2012 Page 16 of 41
in Figure 6 below. It was noted by several participants that dihydroaldrin is not resolved from isodrin if a
lower polarity column (eg DB-5) is used.


Figure 6 GC-FID chromatogram for CCQM-K55.b (reproduced from NIST report)
All participants reported and identified isodrin (2) and dieldrin (3) in the study material. The majority also
reported the presence either by GC or LC or both of an impurity with a long retention time relative to
aldrin, although only five participants identified it as dechlorane (4).
Many participants reported a peak corresponding to dihydroaldrin (5), eluting between aldrin and isodrin
on GC using a DB-17 column or equivalent and at slightly longer retention time than aldrin by LC on
reverse-phase columns. While several participants tentatively identified it as dihydroaldrin based on its
mass spectrum, the NIST were the sole participant to establish the structure assignment by comparison
with an independently synthesised sample. Although the reporting requirements only required a value for
total related structure impurities, all but one participant also provided estimates for the major individual
impurities. The reported values for individual and combined related structure impurities are listed below in
Table 5.

CCQM-K55.b Final Report October 2012 Page 17 of 41
Related substance impurities (mg/g)
Participant Isodrin Dieldrin Dechlorane Total u c
INTI 21.8 2.62 24.4 0.5
VNIIM 21.3 5.2 27.3 0.9
NIM 26.47 3.4 32.5 1.1
INMETRO * * * * 32.7 0.57
UME 25.62 2.94 2.68 32.85 0.047
LNE 28.38 3.53 2.03 33.94 0.46
BIPM 25.5 4.1 4.5 34.4 0.65
HSA 25.9 2.9 4.4 34.6 0.72
NIMT 28.98 3.72 2.1 34.8 1.38
NMIA 26.35 3.16 3.48 34.8 0.32
GLHKSAR 26.71 3.39 1.44 35.3 1.69
KRISS 27 3.15 3.64 35.5 0.11
NIST 26.88 3.19 4.13 36.1 0.8
BAM 26.1 3.2 3.7 36.2 0.05
LGC 28.08 4.08 3.05 36.45 1.83
NMISA 27.77 3.46 4.19 36.9 0.93
NMIJ 26.6 3.46 4.81 37 0.5
CENAM 31.9 3.6 2.65 38.9 2.6

Table 5 – Estimates of total and individual aldrin-related impurities in CCQM-K55.b
* Presence of isodrin, dieldrin and dechlorane reported without individual estimates

For assignment of a KCRV for total organic impurities, it is proposed to use the values reported by the
fifteen participants who observed and included all three major impurities (isodrin, diledrin and
dechlorane) in their total value and exclude the three results that did not report the presence of the long
retention time impurity due to dechlorane.
The mean of the selected results was chosen as the estimate of the KCRV for related structure impurity
content (KCRVRel Subst.). The associated standard uncertainty of the KCRV (uRel Subst.) is the standard
deviation of the mean of the selected data set.
KCRVRel Subst. = 35.4 mg/g;
uRel Subst .= 0.42 mg/g

The results reported by participants with their associated standard uncertainties (k = 1) plotted against the
proposed KCRVRel Subst. are shown in Figure 7.

CCQM-K55.b Final Report October 2012 Page 18 of 41
20
30
40
50
IN
TI
VN
IIM NI
M
IN
ME
TR
O
UM
E
LN
E
BIP
M
HS
A
NI
MT
NM
IA
GL
HK
SA
R
KR
ISS NI
ST
BA
M
LG
C
NM
IS
A
NM
IJ
CE
NA
M
To
ta
l R
el
at
ed
S
ub
st
an
ce
s
(m
g/
g)

Figure 7 Estimates of total related structure impurities in CCQM-K55.b plotted with their reported
standard uncertainties ( uc , k = 1).
The proposed KCRV for this impurity class (KCRVRel. Subst.) (solid red line) is 35.4 mg/g.
Dashed red lines show the KCRV  uRel. Subst. (k = 1).
ii. KCRV for water content in CCQM-K55.b
The values for water content in CCQM-K55.b provided by the participants are set out below in Table 6,
along with a short description of the variant of the Karl Fischer titration method used.

Participant Water content (mg/g) U95% (mg/g) Karl Fischer Method outline
VNIIM 0.11 0.02 Direct addition of solution, 3 x 100 mg
NMIJ 0.31 0.04 Direct addition of solid, 3 x 55 mg
KRISS 0.32 0.14 Direct addition of solid, 3 x 20-30 mg
CENAM 0.4 0.1 Direct addition of solid, 2 x 100 mg
HSA 0.4 0.28 Direct addition of solid, 5 x 8-20 mg
Oven transfer @ 170 C
BAM 0.42 0.09 Oven transfer @ 130 C, 3 x 100-150 mg
NIST 0.44 -0.09/+ 0.17 Direct addition (of soln. ?), 5 x 20-50 mg
GLHK 0.46 0.1 Oven transfer @ 160 & 230 C, 50 mg
LGC 0.47 0.98 Oven transfer @ 100 C, 3 x ?? mg
BIPM 0.5 - 0 /+ 0.58 Oven transfer @ 120 C, 3 x 50 mg
INMETRO 0.54 0.026 Direct addition of solution, 2 x 100 mg
Table 6 – Estimates of water content for CCQM-K55.b

CCQM-K55.b Final Report October 2012 Page 19 of 41

Participant Water content (mg/g) U95% (mg/g) Karl Fischer Method outline
NMISA 0.6 0.22 Direct addition of solid, 3 x 50 mg
NMIA 0.91 3.6 Direct addition of solid, 3 x 20-30 mg
NRC-INMS 1 - 1 /+ 0
NIM 1.24 0.36 Direct addition of solid, 3 x 50 mg
LNE 1.31 0.07 Oven transfer @ 100 C, 3 x 100 mg
UME 2 0.12 Direct addition of solution, 1 x 50 mg
NIMT 6.43 0.4 Oven transfer @ 120 C, 5 x 60 mg
INTI 11.9 0.2 Direct addition of solid, 25 mg
Table 6 (ctd) – Estimates of water content for CCQM-K55.b
All participants used coulometric Karl Fischer titration as the minimum method to obtain the water
content estimate. A mixture of procedures including direct addition into the titration cell as a solid, direct
addition as a solution and sample oven transfer to deliver the water content from a sample of
CCQM-K55.b into the titration cell were used. There was generally good agreement for the presence of a
small but detectable amount of water in the material. No ready explanation is available for the two results
that were appreciably in excess of the median value of 0.5 mg/g. Several participants used other
techniques (TGA, qNMR, elemental analysis) as confirmatory analyses or consistency checks.
Because of the asymmetric spread of results, the median of the combined results for water is proposed as
the KCRV for water content (KCRVH2O) in CCQM-K55.b. The associated standard uncertainty of the
KCRV (uH2O) is assigned as the robust statistical estimate of the standard deviation of the median
(MADe/√n) of the data set
KCRVH2O = 0.47 mg/g;
uH2O .= 0.05 mg/g
The results reported by participants with their associated standard uncertainties (k = 1) plotted against the
proposed KCRVH2O are shown in Figure 8.

Figure 8 Estimates for water in CCQM-K55.b plotted with reported standard uncertainties
(k = 1). The proposed KCRV for water content of CCQM-K55.b (solid red line) is 0.47 mg/g.
Dashed red lines show the proposed KCRVH2O  uH2O (k = 1).

CCQM-K55.b Final Report October 2012 Page 20 of 41

iii. KCRV for VOCs in CCQM-K55.b
Fourteen of the eighteen participants provided estimates for the volatile organics content of
CCQM-K55.b. Each participant who investigated residual solvent content reported a significant
level of methanol in the sample.
GC approaches with detection by headspace and direct MS analysis (GC-MS) or headspace FID (,
in several cases independently cross checked by NMR methods, were used to identify and quantify
the methanol content of the sample. The number of participants now incorporating rigorous
methods to detect residual solvent was encouraging and a significant increase compared with the
earlier CCQM-P20 and CCQM-K55.a comparisons. Given the volatile nature of methanol, which
makes it a challenging compound to quantify, the overall agreement with the proposed KCRV was
also encouraging.
HSA were the only participant to report a methanol content significantly higher than the values
found by other participants. They also commented that the samples they received displayed a
significant level of inhomogeneity. No comments on the variability or instability in the methanol
content of the sample were received from other participants.
The results obtained by the study participants of CCQM-K55.b are listed in Table 7 and shown
graphically in Figure 9.

Participant Methanol
content (mg/g)
U95%
(mg/g)
Method(s)
GLHK 0.9 0.17 HS-GC-MS & GC-MS
NIM 1.67 0.15 HS-GC-MS & HS-GC-FID
NRC-INMS 1.9
2.5
0.6
0.3
qNMR
GC-MS
BAM 2.0 0.1 HS-GC-MS & qNMR
LGC 2.14 0.46 HS-GC-MS & qNMR
NMIA 2.32 1.2 HS-GC-MS & qNMR
NIST 2.33 0.28 qNMR, check by HS-GC-MS
NMISA 2.33 0.0004 HS-GC-TOF & HS-GC-FID
KRISS 2.44 0.26 TGA
BIPM 2.5 0.1 GC-MS, check by TGA & NMR
LNE 2.74 0.18 HS-GC-FID
UME 3.0 0.12 HS-GC-MS & qNMR
NMIJ 3.49 0.08 HS-GC-MS & qNMR
HSA 5.2 0.5 HS-GC-FID
Table 7 – Estimates of residual solvent (methanol) content in CCQM-K55.b

The mean of the results is proposed as the KCRV for VOC content (KCRVVOC) in CCQM-
K55.b. The associated standard uncertainty of the KCRV (uVOC) is assigned as the standard
deviation of the mean of the data set

CCQM-K55.b Final Report October 2012 Page 21 of 41
KCRVVOC = 2.30 mg/g
uVOC .= 0.16 mg/g


Figure 9 Estimates for methanol content reported by participants in CCQM-K55.b plotted with their associated
standard uncertainties (k = 1). The proposed KCRV for residual solvent in CCQM-K55.b (2.30 mg/g,
uVOC 0.16 mg/g) is indicated by the solid red line. Dashed red lines show the KCRVVOC  uVOC (k = 1).


iv. KCRV for non-volatile organics/inorganics content in CCQM-K55.b
The estimates reported for non-volatiles/inorganics content provided by the comparison participants are
listed in Table 8. Using various methods including TGA, ICP-MS, ICP-OES or XRF spectrometry
participants essentially found very low to negligible levels of inorganic material in the sample. The HSA
observed a significant residue after high temperature TGA under non-oxidising conditions. NMIJ found
no significant residue after high-temperature TGA but did detect a significant residue after exhaustive
distillation (100 °C, 90 h, 2.5 x 10-4 Pa). The NMIJ ascribed this distillation residue to a non-volatile
organic residue present in the CCQM-K55.b. As mentioned already, in further studies subsequent to the
original discussion of results the NMIJ provided additional evidence through size-exclusion
chromatography for the presence of an oligomeric organic-based impurity in CCQM-K55.b.
NIST reported the presence of a small level of Si-related material by XRF and GLHK reported Al-related
impurity present at 0.25 mg/g by ICP-MS. GLHK noted that AlCl3 is a commonly used catalyst in the
manufacture of aldrin, which may account for its presence.
In general it appeared that the methods used by the other participants in this case while suitable for
detecting inorganic impurities were insensitive in this case to a significant level of non-volatile organics.

CCQM-K55.b Final Report October 2012 Page 22 of 41
Participant Non-volatiles
content
(mg/g)
U95% (mg/g) Method outline
BIPM 0 0 / 0.06 ICP-MS, cross check by % C,H analysis
KRISS 0 1.8 TGA (160 - 500 °C, 1 hr)
NIMT 0 0.28 TGA (200 - 1000 °C, 20 min under O2)
NMIA 0 2 TGA (120 - 850 °C, 20 min [under O2?])
cross check by % C,H analysis
NMISA 0 0.22 TGA (90 - 800 °C, 10 min [under air])
VNIIM 0 ICP-MS
INMETRO 0.00008 0.000007 ICP-MS
NIM 0.038 0.04 ICP-MS
NIST 0.05 0.02 XRF
NMIJ
(Inorganics)
0.12 TGA (35 - 650 °C, 1 hr under air)
LGC 0.15 0.08 ICP-MS, ICP-OES, TGA (20 - 1000 °C)
GLHK 0.25 0.28 / 0.25 ICP-MS
UME 0.5 0.007 TGA (50 - 1000 °C)
HSA 9.9 2.1 TGA (120 - 850 °C, 30 min under air)
NMIJ
(Organics)
12 2 Exhaustive vacuum distillation (110 °C,
90 h, 2.5x10
-4
Pa)
Table 8 – Estimates of non-volatiles/inorganics content for CCQM-K55.b/CCQM-P117.b
Given that the follow up studies by the NMIJ demonstrated the presence of a significant non-volatile
impurity in CCQM-K55.b, the information available directly from the study is limited to the mean of
the two results for non-volatile organics. It is proposed to use this value as the KCRV for non-
volatiles content (KCRVNV) in CCQM-K55.b. The associated standard uncertainty of the KCRV
(uNV), assigned assuming a rectangular distribution in the range between the two values used for the
KCRV, is 0.58 mg/g (= half range/√3).
KCRVNV = 11 mg/g
uNV .= 0.58 mg/g

The proposed value for total non-volatiles is consistent with the data obtained subsequently by
NMIJ using gel permeation chromatography.
The reported individual values for each participant are given in Table 8 and are shown graphically
in Figure 10 along with the proposed KCRV.

CCQM-K55.b Final Report October 2012 Page 23 of 41

Figure 10 Estimates for combined non-volatiles/inorganics content reported by participants in CCQM-K55.b
plotted with their associated standard uncertainties (k = 1). The proposed KCRV for non-volatiles
in CCQM-K55.b (11 mg/g, uNV = 1 mg/g) is indicated by the solid red line. Dashed red lines show the
proposed KCRVNV  uNV (k = 1).

Key Comparison Reference Values (KCRVs) for Aldrin in CCQM-K55.b
It was agreed by the participants during the discussion of results that, as for the CCQM-K55.a comparison,
assignment of a KCRV for aldrin in CCQM-K55.b based solely on the combined reported results for
overall aldrin content was not justified and would be misleading. After initial discussion at the November
2010 CCQM OAWG meeting, follow-on studies were undertaken to investigate the reason for the
approximate 10 mg/g discrepancy between mass balance and qNMR results. Subsequent discussion of this
data continued at the CCQM OAWG meeting in April 2011 where the NMIJ presented convincing
additional data using in particular gel permeation chromatography to demonstrate that a high molecular
weight impurity (MW > 1000 ) was present at around the 10 mg/g level in CCQM-K55.b.
The comparison coordinator was asked to follow the precedent of the approach used in the CCQM-P20.f
and CCQM-K55.a comparisons to propose individual KCRVs for the mass fraction of each of the
orthogonal classes of impurity present in the comparison material and to use these values to assign an
overall KCRV for aldrin content.
Information on the mass fraction assignments of these major impurities was requested in the comparison
protocol and reporting form from those participants using the mass balance approach to assign aldrin
content.

CCQM-K55.b Final Report October 2012 Page 24 of 41
Assignment of KCRV for Aldrin in CCQM-K55.b
The measurement equation (Eqn. 1) to assign the KCRV of aldrin in CCQM-K55.b (in mg/g) is:

][1000 ..Rel VOCrelsubstNonVolVOCWaterSubstAldrin HHwwwww 
(Eqn. 1)

Aldrinw
= KCRV for mass fraction of aldrin in CCQM-K55.b
..Re Substlw
= KCRV for mass fraction of aldrin-related impurities in CCQM-K55.b
Waterw
= KCRV for mass fraction of water in CCQM-K55.b
VOCw
= KCRV for mass fraction of volatile organic solvents in CCQM-K55.b
NonVolw
= KCRV for mass fraction of non-volatile organics/inorganics in CCQM-K55.b
..SubstlReH
= Correction for between unit inhomogeneity of aldrin-related impurities in the
CCQM-K55.b material. Assigned 0 with associated uncertainty (uH Rel Subst.)
.VOCH
= Correction for between unit inhomogeneity of volatile organic content in the
CCQM-K55.b material. Assigned 0 with associated uncertainty (uH VOC)

Units for reporting mass fraction (
w
) are mg/g throughout.
The standard uncertainty associated with the mass fraction estimate was calculated from equation (2):
222222 )()()()()()(
Re..Subst Rel OrgSolvlSubstNonVolOrgSolvWaterAldrin HHwwwww
uuuuuuu 
(Eqn. 2)
The KCRVs for the impurity classes used for calculation of a mass balance KCRV for aldrin in the
CCQM-K55.b comparison are summarised in Table 9.
Input factor w Proposed KCRV
(mg/g)
n u(KCRV)
(mg/g)
Related structure organics 35.4 15 0.42
Water 0.47 17 0.05
Volatile organics 2.30 14 0.16
Non-volatiles/inorganics 11.0 2 0.58
Homogeneity - related
structure impurities
0.0 large 0.42
Homogeneity – volatile
organics
0.0 large 0.1
Combined value 49.17 0.85
Table 9: KCRV values for impurities used for calculation of aldrin KCRV and associated combined
standard uncertainty in CCQM-K55.b

CCQM-K55.b Final Report October 2012 Page 25 of 41
When substituted into the equations (1) and (2), the KCRV for aldrin content becomes:
][1000 Re.... OrgSolvlSubstNonVolSolvOrgWaterSubstRelAldrin HHKCRVKCRVKCRVKCRVKCRV 
mg/g
= 1000 – [35.4 + 0.47 + 2.3 + 11]) mg/g
= 950.8 mg/g
222222 )()()()()()(
Re.. OrgSolvlSubstNonVolOrgSolvWater SubstRelAldrin HHKCRVKCRVKCRVKCRVKCRV
uuuuuuu 
mg/g


222222 )1.0()42.0()58.0()16.0()05.0()42.0( 
mg/g
= 0.85 mg/g

This is regarded as a conservative estimate for the standard uncertainty of the KCRV.
Figure 11 shows the participant results with their reported standard uncertainties plotted against the
proposed KCRV (solid red line) and its associated standard uncertainty (k = 1). Figure 12 shows the
same results with their expanded uncertainty and the KCRV with the corresponding expanded
uncertainty for an approximately 95% coverage range (dashed red lines).

Aldrin content in CCQM-K55.b
940
950
960
970
980
990
1000
IN
M
S
-N
R
C
N
M
IJ
H
S
A
B
A
M
N
IM
T
N
M
IS
A
C
E
N
A
M
*
L
G
C
N
IS
T
K
R
IS
S
U
M
E
L
N
E
N
M
IA
B
IP
M
G
L
H
K
S
A
R
IN
T
I
N
IM
IN
M
E
T
R
O
V
N
IIM
A
ld
ri
n
(
m
g
/g
)

Figure 11: Mass fraction estimates by participants for aldrin in CCQM-K55.b with their reported combined
standard uncertainty (u). Key Comparison Reference Value for CCQM-K55.b (solid red line) is
950.8 mg/g . The calculated combined standard uncertainty of the KCRV is 0.85 mg/g. Dashed red
lines show KCRV  uc (k = 1)

CCQM-K55.b Final Report October 2012 Page 26 of 41
Aldrin content in CCQM-K55.b
940
950
960
970
980
990
1000
IN
M
S
-N
R
C
N
M
IJ
H
S
A
B
A
M
N
IM
T
N
M
IS
A
C
E
N
A
M
*
L
G
C
N
IS
T
K
R
IS
S
U
M
E
L
N
E
N
M
IA
B
IP
M
G
L
H
K
S
A
R
IN
T
I
N
IM
IN
M
E
T
R
O
V
N
IIM
A
ld
ri
n
(
m
g
/g
)

Figure 12: Mass fraction estimates by participants for aldrin in CCQM-K55.b with reported expanded
uncertainty corresponding (U95%). Key Comparison Reference Value for CCQM-K55.b (solid red
line) = 950.8 mg/g . The expanded uncertainty for 95% coverage range of the KCRV (dashed red
lines) is 1.7 mg/g.

The degree of equivalence of a participant’s result with the KCRV (Di) is given by:
Di = wi – KCRVAldrin
The expanded uncertainty Ui at the approximately 95% coverage level associated with the Di was
calculated as:
22
%95 )()(*2)( Aldrinii KCRVuwuDU 

Table 10 records the degree of equivalence (Di) of each key comparison participant’s result with the
proposed KCRV for aldrin. These results are shown graphically in Figure 13.

CCQM-K55.b Final Report October 2012 Page 27 of 41
-10.0
-5.0
0.0
5.0
10.0
15.0
20.0
25.0
IN
M
S
-N
R
C
N
M
IJ
H
S
A
B
A
M
N
IM
T
N
M
IS
A
C
E
N
A
M
*
L
G
C
N
IS
T
K
R
IS
S
U
M
E
L
N
E
N
M
IA
B
IP
M
G
L
H
K
S
A
R
IN
T
I
N
IM
IN
M
E
T
R
O
V
N
IIM
D
i
(m
g
/g
)
-1.0%
-0.5%
0.0%
0.5%
1.0%
1.5%
2.0%
2.5%

Figure 13: Degree of equivalence (absolute and relative) with the aldrin KCRV for each
participant. Points are plotted with the associated expanded uncertainty in the degree of
equivalence corresponding to an approximately 95% coverage range.

CCQM-K55.b Final Report October 2012 Page 28 of 41

Participant Di (mg/g) UD (mg/g)
NRC-INMS -3.0 6.2
NMIJ -0.7 6.7
HSA -0.4 3.1
BAM 2.2 8.2
NIMT 7.7 3.3
NMISA 9.4 4.2
CENAM 9.9 7.2
LGC 10.1 4.2
NIST 10.2 1.7
KRISS 10.8 2.5
UME 10.9 2.6
LNE 11.2 1.9
NMIA 11.3 5.1
BIPM 11.8 2.1
GLHK 12.3 3.8
INTI 12.9 19.1
NIM 13.8 2.9
INMETRO 16.0 2.0
VNIIM 21.8 2.5

Table 10: Degrees of equivalence Di and expanded uncertainties UD at approximately 95% coverage range
in mg/g for aldrin in CCQM-K55.b

Degree of equivalence plots for impurity KCRVs in CCQM-K55.b
The motivation for assigning KCRVs for the contributing impurity classes in CCQM-K55.b was to
assess the fitness of the individual mass balance methods and to confirm that an overall value for the
main component in agreement with the KCRV for aldrin did not arise simply through cancellation of
errors in the contributing impurity assignments. The derived DoE plots also allow for a visualization
of specific problem areas in cases where agreement with the KCRV for aldrin was not achieved.
The combined DoE plots by participant for each impurity class quantified are shown on the
following pages. To aid in assessment and comparison, the DoE of the overall result for aldrin (cf
Figure 13) is plotted at the right (green data point). Where a participant used a mass balance
approach but provided no information on a particular class of impurities a “pseudo” DoE is shown in
this case as a red data point. This provides information on the validity of the participant’s implicit
assumption that the particular impurity component does not make a significant contribution to the
overall purity.

CCQM-K55.b Final Report October 2012 Page 29 of 41
Mass Balance KCRV DoEs by Participant:
BAM








BIPM









CENAM








Key: ♦ = DoE for reported impurity; ■ = “DoE” when no value reported;
■ = DoE for aldrin in CCQM-K55.b
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOC AldrinOrganics Non-volatiles
BAM
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
BIPM
Aldrin
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
CENAM
Aldrin

CCQM-K55.b Final Report October 2012 Page 30 of 41
GLHK









HSA









INMETRO









Key: ♦ = DoE for reported impurity; ■ = “DoE” when no value reported;
■ = DoE for aldrin in CCQM-K55.b
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
GLHKSAR
Aldrin
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
HSA
Aldrin
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
INMETRO
Aldrin
? 16.0
▲16.0

CCQM-K55.b Final Report October 2012 Page 31 of 41
INTI









KRISS










LGC









Key: ♦ = DoE for reported impurity; ■ = “DoE” when no value reported;
■ = DoE for aldrin in CCQM-K55.b
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
INTI
Aldrin
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
KRISS
Aldrin
-15.0
-10.0
-5.0
0.0
.
.
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
LGC
Aldrin

CCQM-K55.b Final Report October 2012 Page 32 of 41
LNE









NIM









NIM









Key: ♦ = DoE for reported impurity; ■ = “DoE” when no value reported;
■ = DoE for aldrin in CCQM-K55.b

-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
LNE
Aldrin
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOC AldrinOrganics Non-volatiles
NIM
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
NIMT
Aldrin

CCQM-K55.b Final Report October 2012 Page 33 of 41
NIST









NMIA









NMIJ








Key: ♦ = DoE for reported impurity; ■ = DoE for aldrin in CCQM-K55.b
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOC AldrinOrganics Non-volatiles
NIST
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
NMIJ
Aldrin
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOC AldrinOrganics Non-volatiles
NMIA

CCQM-K55.b Final Report October 2012 Page 34 of 41
NMISA









UME









VNIIM









Key: ♦ = DoE for reported impurity; ■ = “DoE” when no value reported;
■ = DoE for aldrin in CCQM-K55.b

-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
UME
Aldrin
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOC AldrinOrganics Non-volatiles
NMISA
-15.0
-10.0
-5.0
0.0
5.0
10.0
15.0
D i
(m
g/g
)
Water VOCOrganics Non-volatiles
VNIIM ? 21.8
Aldrin
▲ 21.8

CCQM-K55.b Final Report October 2012 Page 35 of 41
CONCLUSIONS AND HOW FAR THE LIGHT SHINES
Aldrin was selected to be a representative low polarity, moderately complex organic compounds
capable of analysis by GC. It was anticipated to provide an analytical measurement challenge
representative for the value-assignment of compounds of broadly similar structural characteristics.
For such a relatively impure material, there was excellent agreement between the majority of
participants in both the identification and the quantification of the related structure impurity
content of the sample, confirming the conclusions of CCQM-K55.a that measurement of this
general class of impurities is performed satisfactorily by most NMIs. Where relatively low values
for total organic impurity were reported by an individual participant these were consistent with
underestimation of either the isodrin (2) content or a failure to detect the long retention time
impurity dechlorane (4).
There was also a good level of agreement on the quantification of the water, residual solvent and
inorganics content of the material. Unlike the previous CCQM-P20.f (digoxin) and CCQM-K55.a
(estradiol) comparisons, the majority of participants sought to specifically quantify each of these
impurity components.
As discussed in detail in the main report, the disparity in the final results reported for the aldrin
content, as evidenced from the DoE plot which shows a set of results which overestimate the aldrin
content by approximately 10 mg/g, arose primarily from a failure of most participants using a mass
balance approach to detect the presence of a significant level of non-volatile organic impurity in
the sample. This class of impurity had not been present to any significant extent in any previous
comparisons.
Inspection of the DoE plots by impurity sub-group obtained by participants using the mass balance
approach provides a clear indication of the laboratories that are applying this approach
satisfactorily, apart from missing the non-volatile impurity in this particular instance, and those
which have more general issues to address.
Nevertheless the follow-up discussions revealed that several participants did have an indication
from qNMR data that their mass balance procedure had overestimated the aldrin content, but
decided to accept the mass balance result and assume a hidden bias in the NMR data. By contrast
the laboratories that placed greater value on the qNMR result, notably the NMIJ who invested
significant effort into resolving the discrepancy, were able to find evidence for the presence of
non-volatile organic impurity at the requisite level to bring the mass balance and qNMR results
into agreement.
A secondary issue was that some laboratories need to review their NMR data processing
procedures and software as they obtained a high qNMR value for aldrin, which resulted in a false
degree of confidence in their mass balance results.
In summary, the major conclusions coming out of the comparison were:
 experienced laboratories obtained good levels of agreement in the mass fraction assignments
for related impurities, water and VOC content in CCQM-K55.b. This could be demonstrated
clearly through the equivalence plots relative to the individual KCRVs for individual
participants for these classes of impurities;

CCQM-K55.b Final Report October 2012 Page 36 of 41
 a weakness in direct methods for detecting the presence of significant non-volatile organic
impurities. The inferential methods that had been relied on in previous comparisons
(elemental analysis, NMR, TGA) were not suitable for CCQM-K55.b;
 the varying perceptions prior to the comparison between laboratories of the reliability (or
otherwise) of qNMR for direct assignment of the purity of the main component should be
reviewed in the light of the actual results;
 a need in some cases for improved QC procedures and/or understanding of software
processing issues such that laboratories can have confidence that qNMR data is not biased as
a result of their processing parameters
The results of the comparison provide a strong example of the need to undertake further
investigations when notionally independent methods (mass balance v. qNMR in this instance) give
significantly different main component purity results. A valid explanation for the cause of such
differences should be established before one or other result is discarded. This is particularly so in a
situation where the qNMR result is lower than the mass balance result, as it is not possible in this
case to explain the discrepancy as arising simply from a contribution of NMR signals from
unidentified impurities to the NMR signal being integrated to quantify the main component.
The study shows that in a case where a material is relatively impure both in the level and range of
the impurity components, a capability to assign purity through either a mass balance approach or a
direct qNMR approach with a moderate expanded uncertainty ( U95% < 0.6 % relative) can be
achieved.
“How Far The Light Shines” Statement for CCQM-K55.b
The comparison was intended to demonstrate a laboratory’s performance in determining the mass
fraction of the main component in a high purity organic material. The measurement results should
be indicative of the performance of a laboratory’s measurement capability for the purity
assignment of organic compounds of medium structural complexity (molecular weight 300-500)
and low polarity (pKOW < -2) and for which related structure impurities are best quantified directly
by capillary gas-phase chromatographic techniques.

CCQM-K55.b Final Report October 2012 Page 37 of 41

Annex A : Analysis Space for Organic Primary Calibrators


 CCQM-P20 & CCQM-K55 measurands
 CMC claims for pure substance calibrators or calibration solutions

M
o
lec
u
la
r
Wei
g
h
t


pKOW 

CCQM-K55.b Final Report October 2012 Page 38 of 41
Annex B – Aldrin-related compounds identified in CCQM-K55.b

Cl Cl
Cl
Cl
Cl
ClH
H
H
H
H
H
H H


Cl Cl
Cl
Cl
Cl
Cl
H
H
H H
H
HH
O


Cl Cl
Cl
Cl
Cl
Cl
Cl
Cl
Cl
Cl
Cl Cl




Cl Cl
Cl
Cl
Cl
Cl
H
H
H
H
H
H
HH
H
H

Isodrin (2)
Dieldrin (3)
Dechlorane (4)
Dihydroaldrin (5)

CCQM-K55.b Final Report October 2012 Page 39 of 41

Cl
Cl
Cl
Cl
Cl
Cl
O



Cl
ClCl
Cl
Cl Cl




Cl
ClCl
Cl
Cl Cl
Cl Cl



Cl Cl
Cl
Cl
Cl
Cl



Endrin ketone (6)
Hexachlorocyclopentadiene (7)
Octachlorocyclopentene (8)
Chlordene (9)

CCQM-K55.b Final Report October 2012 Page 40 of 41
Annex C – 1H NMR spectra of CCQM-K55.b
















1H NMR spectrum of OGP.014 in CDCl3 : full scale












1H NMR spectrum of OGP.014 in CDCl3 : expansion of δ 2.5 – 3.5 ppm
Cl Cl
Cl
Cl
Cl
Cl
H
H
H
H
H
H
HH
1
2
3
4
5
6
7
8
9
10
11
12a12s
H-4,5
H-3,6
H-2,7
H-12a
H-12s
CDCl3
1H NMR
PPM 3.50 3.40 3.30 3.20 3.10 3.00 2.90 2.80 2.70 2.60 2.50
SpinWorks 3: BIPM Aldrin OGP-014 005 (10mg) in 0.6ml CDCl3 (over K2CO3) QNP600
file: ...O AWG\K55 stuff\NMR\swe091008\2\fid expt: <zg>
transm itter freq.: 600.133001 MHz
time domain size: 32768 points
width: 6613.76 Hz = 11.0205 ppm = 0.201836 Hz/pt
number of scans: 32
freq. of 0 ppm: 600.130013 MHz
processed size: 32768 complex points
LB: 0.200 GF: 0.0000
Hz/cm: 26.962 ppm/cm: 0.04493
H-3,6 -2,7
Isodrin H-2,7
Methanol
Isodrin H-3,6
Dieldrin H-4,5
Dieldrin H-2,7 & 3,6
Dechlorane?

CCQM-K55.b Final Report October 2012 Page 41 of 41

References
1 Westwood, S., Josephs, R. D., Daireaux, A., Wielgosz, R., et al.: An international comparison of mass fraction
purity assignment of theophylline: CCQM Pilot Study CCQM-P20.e (Theophylline), Metrologia, 46 (2009) 1A,
08019
2 Westwood, S., Josephs, R. D., Choteau, T., Mesquida, C., Daireaux, A., Wielgosz, R., et al: An international
comparison of mass fraction purity assignment of digoxin: CCQM Pilot Study CCQM-P20.f (Digoxin), Metrologia
48 (2011) 1A, 08013.
3 Westwood, S., Josephs, R. D., Daireaux, A., Wielgosz, R., et al; Final report on key comparison CCQM-
K55.a (Estradiol): An international comparison of mass fraction purity of estradiol, Metrologia, 49 (2012)
1A, 08009
4 J. Sangster, Octanol-water Partition Coeffcients: Fundamentals and Physical Chemistry, John Wiley &
Sons, Chichester (1997).