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Copyright © 2001, The National Academy of Sciences Medical Sciences Correlation of breath ammonia with blood urea nitrogen and
creatinine during hemodialysis *Department of Physics and Astronomy, University of California, Los Angeles, CA 90095; and †Department of Nephrology, School of Medicine, University of California, Los Angeles, CA 90095 ‡To whom reprint requests should be addressed:
Department of Physics and Astronomy, 6-130H Knudsen Hall, University of
California, Los Angeles, CA 90095-1547. E-mail:
patel/at/physics.ucla.edu. Contributed by C. Kumar N. Patel Accepted February 5, 2001. Abstract We have spectroscopically determined breath ammonia levels in seven
patients with end-stage renal disease while they were undergoing
hemodialysis at the University of California, Los Angeles, dialysis
center. We correlated these measurements against simultaneously taken
blood samples that were analyzed for blood urea nitrogen (BUN) and
creatinine, which are the accepted standards indicating the level of
nitrogenous waste loading in a patient's bloodstream. Initial levels
of breath ammonia, i.e., at the beginning of dialysis, are between
1,500 ppb and 2,000 ppb (parts per billion). These levels drop very
sharply in the first 15–30 min as the dialysis proceeds. We found the
reduction in breath ammonia concentration to be relatively slow from
this point on to the end of dialysis treatment, at which point the
levels tapered off at 150 to 200 ppb. For each breath ammonia
measurement, taken at 15–30 min intervals during the dialysis, we also
sampled the patient's blood for BUN and creatinine. The breath ammonia
data were available in real time, whereas the BUN and creatinine data
were available generally 24 h later from the laboratory. We found
a good correlation between breath ammonia concentration and BUN and
creatinine. For one of the patients, the correlation gave an
R2 of 0.95 for breath ammonia and BUN
correlation and an R2 of 0.83 for breath
ammonia and creatinine correlation. These preliminary data
indicate the possibility of using the real-time breath ammonia
measurements for determining efficacy and endpoint of hemodialysis. Keywords: end-stage renal disease, breath analysis Expired human breath
has been analyzed extensively by mass spectrometric techniques for the
existence of a variety of trace amounts of volatile organic compounds
and several small inorganic molecules such as ammonia, nitric oxide,
carbon disulfide, and carbon dioxide (1). Of these, several gases
exhaled in human breath, e.g., ammonia, nitric oxide, aldehydes, and
ketones, have been linked to kidney and liver malfunction, asthma,
diabetes, cancer, and ulcers (2–4). Others, such as carbon disulfide,
ethane, butane, and pentane have been linked to neurological disorders,
including schizophrenia (5, 6). A few nascent technologies promise the
ability to detect some of these compounds at the required
parts-per-million (ppm) or parts-per-billion (ppb) concentration levels
while in the presence of other interfering species. Recently, a
chemiluminescence detector is being deployed for quantifying nitric
oxide in human breath (7–9). Of the above afflictions, end-stage renal
failure forces over 197,000 patients who require hemodialysis in the
United States to undergo lengthy, three-times-per-week, often painful,
in-clinic treatment (paid by Medicare) to compensate for the loss of
their kidney functions. Another 28,000 patients undergo peritoneal- or
hemodialysis in their homes. Improper, insufficient, and/or
delayed treatment leads quickly to secondary organ failures and a rapid
death. Our study indicates that a breath ammonia measurement may be
capable of providing patients requiring kidney dialysis and their
physicians a fast, painless, and cost-effective in situ
monitor that measures the progress of dialysis in real time, and which
could potentially improve the quality of renal care. We have assessed
the quantitative measure of ammonia exhaled in human breath as an
instantaneous, noninvasive, and low-cost alternative to blood tests in
evaluating the effectiveness of kidney dialysis. We report results of
deploying a laser-based breath ammonia sensor (100 ppb
ammonia-detection sensitivity) into the University of California, Los
Angeles, kidney dialysis center to correlate the reduction in the
accepted blood markers—creatinine (≈14 mg/dl to ≈5
mg/dl) and blood urea nitrogen (BUN) (≈90 mg/dl to
≈30 mg/dl)—with a reduction in the breath ammonia
concentration from ≈2,000 ppb to ≈200 ppb. We have observed a
monotonic reduction in breath ammonia as the dialysis proceeds and we
present quantitative correlation between breath ammonia and BUN and
creatinine measured in blood samples. Once refined and established, the
use of the breath ammonia sensor can serve (i) as an
endpoint detector for dialysis treatment, (ii) to measure
painlessly the rate of buildup of waste products in blood after
treatment, and (iii) as a means for physicians to rapidly
tailor the dialysis regimen to the changing needs of their patients. Kidney dialysis adequacy is determined presently through the use of a
dimensionless parameter called the urea reduction ratio (URR) that
compares the pre- and postdialysis levels of BUN as determined through
laboratory analyses of blood samples taken at the beginning and at the
end of dialysis treatment:
Experimental Methods Spectroscopic Measurements of Ammonia. Absorption and emission of light by molecules has long been used as a
means of identifying which molecules are present in a mixture
(qualitative analysis) and in what concentration (quantitative
analysis). Most molecules with two or more atoms show distinct
absorptions in the infrared region of the spectrum, generally defined
as light with a wavelength between 1 μm and 15 μm (1 μm =
10−6 m). These features can be extremely sharp
for molecules that are in the gas phase and at low pressure, enabling
both the qualitative and quantitative assays with very high selectivity
of species through their so-called “fingerprint” absorptions. Laser spectroscopy has been used extensively for detection of a large
number of industrially produced pollutant gases such as NO,
NO2, NH3,
SO2, and CH4. Many of these
gases are found in large concentrations at their sources, e.g., nitric
oxide at the tailpipe of an automobile (12), and at very low
concentrations in ambient atmosphere and stratosphere (13). The
concentration of an unknown sample is determined by characterizing the
optical absorptivity of a sample of known concentration. A number of
techniques have been developed to obtain the necessary spectroscopic
parameters for a wide variety of molecular gases. These methods include
conventional measurements of light throughput, calorimetry, cavity-ring
down spectroscopy (refs. 14 and 15 and references cited in ref. 15),
and thermal distortion spectroscopy (ref. 16 and references cited
therein). Of these, calorimetric techniques have been shown to be
widely applicable for ultra low-absorption measurements, leading to
sub-ppb detection of many gaseous components (17). There is increasing evidence that the chemical composition of expired
breath can be an accurate, timely, and painless indicator of the health
of an individual (1). The exhaled gases can be used as surrogates for
inferring the makeup of blood and the functioning of vital organs. Here
we describe our early results on the application of optoacoustic
spectroscopy for the detection of minor constituents of human breath of
patients undergoing hemodialysis (see ref. 18 for a preliminary
report). The experimental scheme is shown in Fig.
Fig.1.1
Ammonia Detection. We use a sealed-off, radiofrequency excited CO2
laser whose operating wavelength can be line switched from R40 of the
9-μm band to P50 of the 10-μm band (by using an intracavity
grating), giving us laser operation on more than 120 discrete
frequencies. These transitions are separated by 1–2
cm−1 and the laser frequency, therefore, is not
continuously tunable. Nonetheless, we take advantage of pressure
broadening of the absorbing species by choosing the gas pressure
appropriately (see ref. 18 for additional details). In particular, we
operate the optoacoustic cell at nearly atmospheric pressure. At this
pressure, ammonia presents a large absorption at a particular
CO2 laser wavelength and is transparent at
another nearby laser line. We divert a small portion of the laser beam
into another optoacoustic cell, which contains a reference mixture of
ammonia in air, and normalize the breath measurements to this
calibrated mixture. At the selected wavelength of the
CO2 laser, there are two additional components in
human breath that could interfere with NH3
absorption. These are saturated water vapor at human body temperature
(37°C) and CO2 (≈4% by volume). We have
found that water vapor interference is negligible at the wavelength
chosen for NH3 absorption measurements (20).
Independent measurements of breath on another laser line show that the
CO2 level is relatively constant. Hence, the
background absorption signal caused by breath CO2
and H2O is assumed to be relatively constant, and
this amount is subtracted as a constant offset for all measurements.
Patients requiring dialysis do dehydrate during treatment. We examined
the effect of moisture content through a “synthetic patient”
protocol as part of the system calibration procedure (vide
infra). These data indicate that moisture content is a
second-order effect in the measured signal, and hence we believe the
assumption of a constant (and small) water-vapor contribution to be
valid. This scheme allowed us to measure NH3
levels as low as 100 ppb in human breath by using a 3-second data
integration time. The breath ammonia measurements involve the patient breathing into a
lightweight disposable mouthpiece (or a face mask) and hose that
conveys the breath to the instrument. The instrument continuously
analyzes the sample and displays an absolute measure of the ammonia
concentration in ppb. An accurate measurement can be obtained in well
under a minute, the time required for the breath sample to reach the
measurement chamber. Clinical Background Kidney Failure and Malfunction. Kidney failure can be a result of diseases such as diabetes,
glomerulonephritis, certain viral infections, and/or direct
trauma to the organ. Nephrons, the filtering agents that remove
nitrogen-bearing wastes from the blood, are damaged either partially or
fully during kidney failure. Renal disease is perforce signaled by a
rise in the nitrogen-bearing compounds in the patient's blood stream,
with serious consequences to other organs and to the patient's
lifespan. Two of the important compounds are BUN
[CO(NH2)2] and creatinine
(2-amino-1,5-dihydro-1-methyl-4H-imidazol-4-one). Patients
with end-stage renal disease (ESRD) must have their blood filtered
through reverse osmosis every other day for several hours. In the U.S.,
dialysis times range from 2 to 5 h. Standard practice during a
dialysis session involves withdrawing 3–5 ml of blood immediately
before and immediately after treatment, and then sending the samples
for analysis with typically a 1-day turnaround time. The decrease in
concentration of BUN is used to compute the URR, as defined earlier. Under normal circumstances, the predetermined period of hemodialysis
functions reasonably well but it does not account for the patient's
change in lifestyle or any change of diet. There is, however,
substantial agreement among nephrologists that the present methods of
determining dialysis times and sufficiency are too empirical. The blood
workups do provide useful long-term information about anemia and other
conditions but they are not a source of timely information on the
progress during any particular session. Dialysis is a chemical
titration that presently has no effective real-time endpoint detector. Nitrogenous Wastes and Ammonia. In a healthy individual, ammonia and ammonium ions are converted to
urea in the liver through the enzymatically moderated and energetically
expensive linked urea and citric acid cycles identified by Krebs and
Henseleit (21). The urea is then transported through the bloodstream to
be excreted into urine by the kidneys. The reversibility of the process
requires an equilibrium concentration of ammonia related to the BUN
loading of the blood. As small molecules, ammonia and ammonium ions can
penetrate the blood–lung barrier, mix, loft, and appear in exhaled
breath. Given a reliable correlation between breath ammonia and blood
markers, we can use breath ammonia concentration as an instantaneous
tracer of nitrogen-bearing wastes in the human body and provide
(i) an important real-time indicator of the efficacy of the
dialysis treatment and (ii) a reliable and real-time
endpoint detector of the level of BUN in the blood of the patient with
ESRD to determine an acceptable termination of the dialysis session.
The before and after measurements also provide URRs for comparison with
the accepted standards. Results and Discussion Synthetic Patient. Fig. Fig.22
Patients with ESRD. By using the instrument described above, we successfully measured the
breath ammonia levels of seven patients undergoing dialysis (in the
University of California, Los Angeles, dialysis center) while taking a
fiduciary blood sample concomitant with each breath measurement. Fig.
Fig.33
The most critical test is the correlation of breath ammonia with
constituents of blood that are used traditionally as the measures of
kidney failure in patients with ESRD. Therefore, we collected data on
BUN and creatinine at the same time as breath ammonia measurements were
carried out. Unlike breath ammonia data that were available
instantaneously, the BUN and creatinine data were received 12–24 h
after the blood samples were sent for analysis. Figs.
Figs.66 Returning to Fig. Fig.3,3 Fig. Fig.88
Conclusion: Ammonia Detection in Breath. Quantifying the level of ammonia in exhaled breath serves two vital
functions: (i) It can be used as a surrogate for elevated BUN, which,
along with the creatinine level in a patient's blood, is the accepted
indicator of kidney malfunction. Our preliminary measurements are among
the very few quantitative data sets correlating breath ammonia with BUN
and creatinine. No correlations have been made yet with glomerular
filtration rates, but these will be acquired once the breath ammonia
instrument is deployed in planned clinical studies of individuals
at-risk for kidney failure. (ii) The breath ammonia level can be used for determining
the exact time necessary for the desired degree of dialysis for a
patient with ESRD at every session. The breath ammonia monitor will
provide crucial information about when a dialysis treatment may be
stopped, i.e., detect an endpoint. The ability of such instrumentation
to detect partial kidney failure will depend on quantitative
correlation between breath ammonia and BUN, creatinine, and glomerular
filtration rates. In the long run, breath ammonia measurement could
serve as a broad noninvasive screen for incipient kidney failure, as
well as a monitor of kidney functions in at-risk populations such as
diabetics and hypertensives. Acknowledgments We thank Professor Gantam Chaudhuri for technical discussions of
the importance of ammonia in human organ functions and disorders. Footnotes §Consider two scenarios for a desired
URR of 70%. The first example is that of a patient whose predialysis
BUN is 100 mg/dl and whose postdialysis BUN is 30 mg/dl. A second
example involves a predialysis BUN of 200 mg/dl and a postdialysis BUN
of 60 mg/dl. Both of these treatments will yield a URR of 70% but for
the second case, the patient could be at a significant long-term risk
if the BUN stays above 60 mg/dl for long periods of time. References 1. Phillips M, Herrera J, Krishnan S, Zain M, Greenberg J, Cataneo R. J Chromatogr. 1999;B729:75–88. 2. Alving K, Weitzberg E, Lundberg J M. Eur Respir J. 1993;6:1368–1370. [PubMed] 3. Paredi P, Biernacki W, Invernizzi G, Kharitonov S A, Barnes P J. Chest. 1999;116:1007–1011. [PubMed] 4. Atherton J C, Spiller R C. Gut. 1994;35:723–725. [PubMed] 5. Phillips M, Sabas M, Greenberg J. J Clin Pathol. 1993;46:861–864. [PubMed] 6. Phillips M, Erockson G A, Sabas M, Sith J P, Greenberg J. J Clin Pathol. 1995;48:466–469. [PubMed] 7. Fontijn A, Sabadell A J, Ronco R J. Anal Chem. 1970;42:575–579. 8. Palmer R M J, Ferrige A G, Moncada S. Nature (London). 1987;327:524–526. [PubMed] 9. Lundberg J O N, Farkas-Szallasi T, Weitzberg E, Rinder J, Lindholm J, Anggard A, Holfelt T, Lundberg J M, Alving K. Nat Med. 1995;1:370–373. [PubMed] 10. Clark W R, Rocco M V, Collins A J. Blood Purif. 1997;15:92–111. [PubMed] 11. National Institutes of Health. Hemodialysis Dose and Adequacy. Bethesda, MD: National Institutes of Health; 1999. 12. Kreuzer L B, Patel C K N. Science. 1971;173:45–47. [PubMed] 13. Patel C K N, Burkhardt E G, Lambert C A. Science. 1974;184:1173–1176. 14. O'Keefe A, Deacon D A G. Rev Sci Instrum. 1988;59:2544–2551. 15. Scherer J J, Paul J B, O'Keefe A, Saykally R J. Chem Rev (Washington, DC). 1997;97:25–51. [PubMed] 16. Bailey R T, Cruickshank F R. In: Photoacoustic, Photothermal, and Photochemical Processes, Topics in Current Physics. Hess P, editor. Vol. 46. Berlin: Springer; 1989. pp. 37–60. 17. Patel C K N. In: Monitoring Toxic Substances, ACS Symposium Series. Schuetzle D, editor. Vol. 94. Washington, DC: Am. Chem. Soc.; 1978. pp. 177–194. 18. Patel C K N, Narasimhan L R, Goodman W G. In: The Biology of Nitric Oxide, Part 7. Moncada S, Gustafsson L E, Wiklund N P, Higgs E A, editors. London: Portman Press; 2000. p. 27. 19. Kenyon N D, Kreuzer L B, Patel C K N. Science. 1972;177:347–349. [PubMed] 20. Rothmann L S, Rinsland C P, Goldman A, Massie S T, Edwards D P, Mandin J Y, Schroeder J, McCann A, Gamache R R, Wattsin R B, et al. J Quant Spectrosc Radiat Transfer. 1998;60:665–710. 21. Lehninger A L, Nelson D L, Cox M M. Principles of Biochemistry. 2nd. Ed. New York: Worth; 1993. pp. 514–520. 22. Davies S, Spanel P, Smith D. Kidney Int. 1997;52:223–228. [PubMed] |
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Eur Respir J. 1993 Oct; 6(9):1368-70.
[Eur Respir J. 1993]Gut. 1994 Jun; 35(6):723-5.
[Gut. 1994]J Clin Pathol. 1993 Sep; 46(9):861-4.
[J Clin Pathol. 1993]J Clin Pathol. 1995 May; 48(5):466-9.
[J Clin Pathol. 1995]Nat Med. 1995 Apr; 1(4):370-3.
[Nat Med. 1995]Blood Purif. 1997; 15(2):92-111.
[Blood Purif. 1997]Science. 1971 Jul 2; 173(991):45-7.
[Science. 1971]Chem Rev. 1997 Feb 5; 97(1):25-52.
[Chem Rev. 1997]Science. 1972 Jul 28; 177(46):347-9.
[Science. 1972]Kidney Int. 1997 Jul; 52(1):223-8.
[Kidney Int. 1997]