methodological aspects on measurement of clara cell protein in urine as a biomarker for airway...
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60 L. ANDERSSON ET AL.
Copyright © 2006 John Wiley & Sons, Ltd. J. Appl. Toxicol. 2007; 27: 60–66
DOI: 10.1002/jat
JOURNAL OF APPLIED TOXICOLOGYJ. Appl. Toxicol. 2007; 27: 60–66Published online in Wiley InterScience(www.interscience.wiley.com) DOI: 10.1002/jat.1184
Methodological aspects on measurement of Clara cellprotein in urine as a biomarker for airway toxicity,compared with serum levels
Lena Andersson,1,* Per-Arne Lundberg2 and Lars Barregard1
1 Department of Occupational and Environmental Medicine, Sahlgrenska University Hospital and Academy, GöteborgUniversity, Göteborg, Sweden
2 Clinical Chemistry, Sahlgrenska University Hospital, Göteborg, Sweden
Received 7 July 2006; Revised 22 September 2006; Accepted 25 September 2006
ABSTRACT: The Clara cell protein CC16, secreted from Clara cells in the lung, is discussed as a potential biomarker
for toxic effects on the airways. An increased concentration of CC16 in serum may be caused by increased permeability
of the lungs, caused by high levels of air pollution. Since CC16 is eliminated by renal excretion, it may be possible to use
urine instead of serum samples. Few studies have been conducted on urinary CC16 (U-CC16), however.
The aim was to investigate the optimal way of sampling and quantifying CC16 in urine samples and compare CC16
in human serum and urinary samples. Repeated sampling was performed in two groups of healthy subjects. First morning
urine, 24 h urine, and matched blood and urine samples were collected.
The excretion of U-CC16 increased over the day, e.g. from 0.08 µµµµµg h−−−−−1 in the morning to 0.28 µµµµµg h−−−−−1 in daytime and
0.16 µµµµµg h−−−−−1 in the evening (medians in males). Morning samples (µµµµµg h−−−−−1) from males properly reflected the 24 h excretion
(r ===== 0.91). The best correlation with 24 h excretion was obtained with creatinine-corrected first morning urine samples
(r >>>>> 0.9). Generally, females had lower excretion of CC16 than males (medians 2.5 µµµµµg 24 h−−−−−1 in females and 16 µµµµµg 24 h−−−−−1
in males). There was significant intraindividual variation, but the interindividual variation was larger in both groups.
There was an association between serum CC16 (S-CC16) and U-CC16 in morning samples. With optimal methods for
sampling U-CC16, urine samples may be used in experimental studies of air pollution. Copyright © 2006 John Wiley &
Sons, Ltd.
KEY WORDS: Clara cell protein; CC16; methodological study; urine sampling
* Correspondence to: L. Andersson, Department of Occupational and
Environmental Medicine, Sahlgrenska University Hospital and Academy,
P.O. Box 414, S-405 30 Göteborg, Sweden.
E-mail: [email protected]
excretion before U-CC16 can be used as a biomarker. In
the literature (e.g. Bernard et al., 1993), several factors
have been shown to affect the levels of CC16 in urine.
The most important are CC16 originating from the pros-
tate (which also secretes CC16), renal function and preg-
nancy. The first portion of urine from men contains CC16
from the prostate (Bernard et al., 1992). The size of the
portion affected by postrenal excretion has not been
quantified. The excretion from the prostate must be elimi-
nated from the urine sample before it can be used as a
surrogate for serum.
When analysing urinary proteins, it is an advantage if
the excretion rate (µg h−1) can be quantified from prefer-
ably a 24 h collection. However, an entire 24 h period of
urine collection can be problematic in field studies. Nor-
mally, spot urine is used and the concentration is often
corrected for creatinine or specific gravity (SG) to com-
pensate for the dilution (Carrieri et al., 2001). No data
were found on the association between creatinine-
corrected levels of CC16 and excretion rates, the variabil-
ity in the excretion of CC16 in urine within and between
individuals, and storage stability. The aim of this study
was to evaluate optimal methods of determining CC16 in
urine by exploring the impact of the postrenal excretion,
Introduction
The Clara cell protein CC16 is secreted from the Clara
cells to the epithelial lining fluid of the lung and is
transported up along the bronchiolar tree. Hermans and
Bernard (1999) report that CC16 can leak to serum
through the lung epithelial barrier. It has been shown that
high levels of air pollution may increase the permeabil-
ity of the lung epithelium (Broeckaert et al., 2000). Con-
sequently, serum CC16 (S-CC16) has been used as a
non-invasive marker in different studies of effects of air
pollution on the airways. Recently, the use of urinary
CC16 (U-CC16) was investigated as well (Timonen
et al., 2004).
In large-scale studies, urine sampling offers several
advantages compared with serum sampling. The non-
invasive urine samples are more readily accepted and the
costs are lower. It is, however, necessary to clarify the
renal handling of the protein and factors affecting its
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METHODOLOGICAL ASPECTS FOR MEASUREMENT OF CC16 61
Copyright © 2006 John Wiley & Sons, Ltd. J. Appl. Toxicol. 2007; 27: 60–66
DOI: 10.1002/jat
first 100 ml of the sample before collecting the urine.
This volume was taken into account when the total vol-
ume was recorded. Replicate samples (5 ml) were taken
directly from all fresh portions and transferred to
polypropylene centrifugation tubes (Sarstedt Australia
Pty. Ltd., Ingle Farm, Australia) and stored cold (4 °C)
until analysis (max 7 days). Samples used for stability
control were immediately frozen (−20 °C) and analysed
after 2 weeks and after 2 months. Samples from day 1
were used for the study of postrenal excretion. Samples
from day 2 were used for examination of the variability
within days. First morning samples from day 1 and 2
were used for calculation of variability between days. All
samples from day 1 and 2 were used for a study of the
association between excretion rates and concentrations in
samples corrected for creatinine and SG, respectively.
Group B. On day 1, one sample was taken from the
first morning urine. The second sample was taken after
6 h, and another, from the next morning’s first urine
(Table 1). The samples were used for studies of stability,
variability within subjects between days, and associations
between S-CC16 and U-CC16. Samples used for stabil-
ity control were frozen (−20 °C) and analysed after
6 months.
Blood Sampling
Group B. The first blood sample was taken 2 h after
the first morning urine sample. The second serum sample
was taken in the afternoon, and the third, on the next
morning 2 h after the urine sample (see Table 1). The
whole procedure was repeated 1 week later. For 13 of
the 24 subjects (six males and seven females), blood
samples was also taken at noon (Fig. 4). All blood
samples were collected by venipuncture in vacuum tubes
(BD Vacutainer™, Franklin Lakes, NJ, USA). The serum
samples were used to study the association between
matched blood and urine samples, and the variability of
S-CC16 within and between days.
Determination of Serum and Urinary CC16
Analyses of CC16 were performed using the Human
Clara Cell Protein ELISA kit from BioVendor
(BioVendor Laboratory Medicine, Inc., Brno, Czech
Republic). Standard and sample solutions were incubated
for 1 h in microtiter wells coated with rabbit polyclonal
antibodies against human CC16. After washing, biotin-
labeled antibodies against CC16 were added, followed
by thorough washing, and addition of Streptavidin-
horseradish-peroxidase. After 1 h incubation and a final
washing, the conjugate reacted with H2O2-tetramethyl-
benzidine. The reaction was stopped by adding an acidic
solution before absorbance was measured at 450 nm. The
Table 1. Urine (U) and serum (S) sampling for deter-mination of Clara cell protein in Group A and Group B
Group A Group B
Day 1 Day 2 Day 1 Day 2
Morning U U U, S U, S
Noon U U U, Sa U, Sa
Afternoon U S S
Evening U
Next morning U, S U, S
a Serum samples taken from 13 of the 24 subjects for the study of diurnal
S-CC16 variation. Morning samples were taken about 8 am, noon samples
about 2 pm and afternoon samples at about 5 pm.
and establishing the optimal time for sampling. Also
examined were the storage stability and the correlation
between matched samples of urine and serum.
Methods
Subjects
Group A. For a detailed study of U-CC16, 20 healthy (no
diabetes, hypertension, or airways or kidney diseases),
non-smoking subjects (ten female and ten male, mean
age 35 years, range 22–57 years) were examined.
Group B. To study CC16 in matched samples of serum
and urine, 24 healthy, nonsmoking subjects (13 female
and 11 male, mean age 37 years, range 21–57 years)
were recruited.
All subjects were recruited from the staff of the
Department, and they filled in a questionnaire about
age, smoking habits, and possible diseases or medication.
The study was approved by the Ethical Committee of
Göteborg.
Postrenal Excretion
All male subjects in group A separated their first urine
sample in three portions of 50 ml each and a fourth por-
tion with the remaining urine. This allowed quantification
of the postrenal excretion in every portion.
Urine Sampling
Group A. On day 1, one sample was taken from the first
morning urine. Another sample was taken before noon,
according to the scheme in Table 1. During day 2, sam-
ples from every urine portion during 24 h were collected
and classified as first morning, noon, afternoon, and
evening samples. All urine samples were timed, and the
total volumes recorded. After the assessment of postrenal
excretion (see Results), the male subjects discarded the
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62 L. ANDERSSON ET AL.
Copyright © 2006 John Wiley & Sons, Ltd. J. Appl. Toxicol. 2007; 27: 60–66
DOI: 10.1002/jat
absorbance is proportional to the con-centration of
CC16. Calibrators with target values in the ranges 5.0–
9.4 µg l−1 and 15.8–23.7 µg l−1 were provided in each kit
and used at the start and at the end of the assay in every
run. Our results were always within the accepted range.
Precision, as assessed in duplicate samples within runs,
was considered acceptable with a coefficient of variation
of 11%.
For both serum and urine samples, 4 µl of undiluted
sample was mixed with 96 µl dilution buffer directly in
the wells. To evaluate samples with low U-CC16, new
analyses with less diluted samples were performed. The
limit of detection was <0.04 µg l−1, defined as such a con-
centration of Clara cell protein giving absorbance higher
than mean absorbance of blank: Ablank + 3 × SDblank. This
was tested in our own laboratory as well.
Determination of Creatinine and Specific Gravity
Analyses of creatinine were performed in fresh urine
using the Jaffé method (Roche Diagnostics, limit of
detection 0.01 mmol l−1). Specific gravity was measured
in fresh urine with a Ceti, Digit 012 refractometer
(Medline, Oxfordshire, UK).
Data Analysis
Excretion rates of CC16 were calculated from the
concentration, volume and sampling time for each urine
portion. Moreover, all urine samples were corrected for
creatinine and SG. Specific gravity calculations were
performed with SGstandard = 1.020. Precision (repeatability)
was assessed from analyses of duplicates from the same
urine or serum samples in the same run.
In the descriptive analyses performed, S-CC16 levels
were found to be approximately normally distributed,
while the distribution of U-CC16 was skewed. The vari-
ability in CC16 within individuals was examined and the
coefficient of variation (CV) was calculated on first
morning urine portions (excretion rates and creatinine-
corrected concentrations) and serum morning samples on
different days in each subject. The total variability in
S-CC16 and log-transformed U-CC16 was partitioned
within and between subjects using PROC NESTED (SAS
Institute, Inc., Cary, NC, USA). The CC16 excretion
rates as well as concentrations corrected for creatinine or
SG in first morning or daytime urine samples were com-
pared with the 24 h CC16 excretion using linear regres-
sion and Pearson’s correlation coefficient. The same
technique was used for comparison of matched serum
and urine samples. Statistical analyses were performed
using the PROC NESTED and PROC VARCOMP pro-
cedures in the SAS System, version 9.1 (SAS Institute,
Inc., Cary, NC, USA).
Results
Postrenal Excretion
In the majority of male subjects, CC16 concentrations
were higher in the first two urine portions (50 ml each).
Stabilization was reached in the third and fourth portion.
The CC16 level in the first portion was three to 200
times higher than the concentration in the third portion.
There was a statistically significant difference between
the second and third portion but no statistically significant
difference was detected between the third and fourth
portion. Therefore, the first 100 ml of each male urine
collection was discarded in all subsequent samples. Male
subjects were supplied with a plastic cup with the 100 ml
level marked. Thus the effect of CC16 originating from
the prostate was considered to be eliminated.
Excretion Rate
The CC16 excretion rate was significantly higher during
day and evening than during the night (Fig. 1). It
was more common for values to be below the limit of
detection in first morning urine samples than in day and
evening samples. The total 24 h excretion was much
higher in men (median 16 µg) than in women (median
2.5 µg) (not shown in the Figure).
Spot Urine Samples versus 24 h Collections
For male subjects, the highest correlation between the
excretion rate at different times of the day and the total
24 h excretion was seen in first morning samples (r =0.91, Fig. 2). The same correlation was not seen in
noon and evening samples (r = 0.41 and r = 0.63, respec-
tively). In female subjects, the correlation coefficients
were >0.98 for all times of the day. For creatinine-
corrected levels (µg g−1), the highest correlation with the
total 24 h excretion of U-CC16 (µg 24 h−1) was again
found in first morning samples (females r = 0.85, males
r = 0.98) compared with samples taken at noon (females
r = 0.64, males r = 0.67) (Fig. 3a and 3b, respectively).
The correlation was high also for the male subjects’ first
morning samples corrected for SG (females r = 0.16,
males r = 0.98).
Variability Within and Between Individuals
To study variability, first morning samples from two
different days were used in subjects (groups A and B)
with detectable values in both first morning samples
(n = 32). About 90% of the total variability was variabil-
ity between individuals and the remaining 10% was
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METHODOLOGICAL ASPECTS FOR MEASUREMENT OF CC16 63
Copyright © 2006 John Wiley & Sons, Ltd. J. Appl. Toxicol. 2007; 27: 60–66
DOI: 10.1002/jat
Figure 1. Median values of CC16 excretion (µg h−1), with 10, 25, 75– and 90 percentiles, in ten female andtenmale subjects at different times of the day
variability within individuals. Within-subject variability
can also be expressed as relative standard deviation
(RSD) in untransformed U-CC16, which was 63%
between days (59% and 42%, respectively, for male and
female subjects).
Figure 2. Association between excretion rates in firstmorning urine samples and the 24 h excretion in males(Pearson r = 0.91) and females (r = 0.98)
Precision and Storage
In 46 fresh urinary samples with a median concentration
of 0.9 µg l−1 (range 0.04–33.8 µg l−1), the CV for determi-
nation of CC16 in duplicates was 11%. To assess storage
stability, 40 samples were used. After both 2 weeks
and 2 months, no significant decrease in concentrations
was seen (point estimates 114% and 109% of the initial
concentrations), but the precision (reproducibility)
decreased (CV 22% and 26%, respectively) when paired
results from fresh and stored samples were compared. For
13 of the subjects in group B, urine samples were also
analysed after 6 months. Again, here was no significant
decrease in concentrations (point estimate 95%) but the
reproducibility was not satisfactory (CV 57%).
Variability of CC16 Levels in Serum
These calculations are based on the 13 subjects in group
B where a total of four serum samples was taken;
morning, noon, afternoon and the next morning, to study
diurnal variation. The level of serum CC16 decreased
over the day despite sex, i.e. in the opposite direction
compared with urine (Fig. 4). In the morning the con-
centrations ranged from 2.0 to 14.5 µg l−1 (mean 7.5, SD
2.7). The median S-CC16 was lowest in the noon
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64 L. ANDERSSON ET AL.
Copyright © 2006 John Wiley & Sons, Ltd. J. Appl. Toxicol. 2007; 27: 60–66
DOI: 10.1002/jat
Figure 3. Associations between creatinine-correctedvalues and the 24 h urinary CC16 (U-CC16) excretion(µg 24 h−1). Pearson correlation coefficients were 0.98(first morning) and 0.67 (noon) in males (a) and 0.85(first morning) and 0.64 (noon) in females (b)
samples. However, when calculating the individual
changes, the mean CC16 decrease was 12% in the second
serum sample (6 h after the morning sample) and 17% in
the third sample (9 h after morning sample). A separate
analysis of all 24 subjects showed a mean decrease
of 25% in the afternoon sample. The within-subject vari-
ability for S-CC16 in morning samples was 22% of the
total variability, 78% being variability between subjects.
Consequently, matched serum morning samples on differ-
ent days showed high correlations, CV 17%.
Urinary CC16 versus Serum CC16
Only 19 of 24 the subjects had values over the limit of
detection in both first morning urine samples. Also, one
Figure 4. Diurnal variation in serum levels of CC16,with median values and 10, 25, 75– and 90 percentiles,in 13 subjects
male subject had indications of renal tubular damage
(high excretion of low molecular weight proteins), his
data were not included. Therefore the calculations are
based on 18 subjects. There was a strong linear associa-
tion (r = 0.76, P = 0.0003) between the mean (n = 2)
CC16 excretion rates in the first morning urine samples
and the mean (n = 2) CC16 concentrations in serum
as shown in Fig. 5. There was no similar association
between the CC16 levels in daytime serum samples (9 h
after morning samples) compared with U-CC16 samples
(6 h after the morning urine sample), (r = 0.34, P = 0.12).
Note, however, that daytime serum and urine samples
were not perfectly matched in time.
Figure 5. Association (Pearson r = 0.76) between themean urinary CC16 (U-CC16) from two morning urinesamples and the mean serum CC16 (S-CC16) from twomatched morning serum samples
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METHODOLOGICAL ASPECTS FOR MEASUREMENT OF CC16 65
Copyright © 2006 John Wiley & Sons, Ltd. J. Appl. Toxicol. 2007; 27: 60–66
DOI: 10.1002/jat
with 24 h excretion was obtained with creatinine-
corrected first morning urine samples. In summary,
if spot urine samples are used, we recommend first
morning samples, either timed with calculation of excre-
tion rates per hour, or creatinine-corrected (or both). For
males, the first 100 ml should be discarded.
Serum CC16
In agreement with a previous study (Helleday et al.,
2006), a decrease in S-CC16 concentration during
daytime was found. By contrast, it was found that the
excretion of U-CC16 increased over the day. Possibly
this could be the reason for the decrease in S-CC16.
Morning serum samples from different days within
subjects showed relatively stable CC16 levels, which is
an advantage when S-CC16 is to be used as a marker in
epidemiological or experimental studies.
Urinary CC16 versus Serum CC16 as a Marker forEffects on the Airways
Although some female U-CC16 levels were below the
detection limit, there was a correlation between serum
and urinary levels of CC16 (Fig. 5). Consequently,
U-CC16 could be used as a surrogate for S-CC16. The
urinary levels were, however, less stable than serum
levels on different days within individuals and there are
still question marks surrounding postrenal excretion,
sampling time and diluted samples. The variation
between individuals was also large, probably larger than
it would be after exposure to air pollution. Therefore, to
compare a group of individuals, large populations will be
needed. On the other hand, since there is an association
between S-CC16 and U-CC16 levels, this opens up an
interest in further investigating the use of urine samples.
In experimental studies the variability within individuals
is more important. Power calculations were performed
with a paired t-test with a normal approximation for α =0.05 based on our geometric group mean in U-CC16
of 0.04 in 32 subjects (the t-test was applied to log-
transformed U-CC16 levels). There will be 80% power
to detect a 50% increase in geometric mean U-CC16 in
a group of individuals (n = 32) before and after exposure
to some factor.
Acknowledgement—Eva M. Andersson is acknowledged for statisticaladvice.
References
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Discussion
The present study shows both possibilities and limitations
in the use of U-CC16. It is an easy sampling method
and CC16 seems to be stable in frozen urine after
2 months of storage. The repeatability was good (CV
11%) for fresh samples, but the precision deteriorated
somewhat after storage. In thawed samples, the precipi-
tate was solved carefully and considered homogenous.
Although, since the amount used in the ELISA was
only 4 µl, it might be less homogenous and therefore
CV increased. The samples from group B, stored for
6 months, showed decreased levels of CC16. The excre-
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Factors affecting Urinary Excretion of CC16
The majority of the female subjects had low U-CC16,
which has been observed previously (Bernard et al.,
1993; Timonen et al., 2004). The high CC16 levels
among some men may be explained by some CC16
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for both female and male subjects. The best correlation
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