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Departments of 1 Medical Physics and 2 Anesthesiology and Critical Care Medicine, Memorial Sloan-Kettering Cancer Center, New York, New York 10021; and 3 Department of Anesthesiology and Intensive Care, University of Ferrara, Ferrara, Italy 44100
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ABSTRACT |
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Conventional gas-exchange instruments are
confined to the measurement of O2 consumption
(
O2) and CO2 production
(
CO2) and are subject to a variety of
errors. This handicaps the performance of these devices at inspired
O2 fraction (FIO2) > 0.40 and limits their applicability to indirect calorimetry only. We
describe a device based on the automation of the Douglas bag technique that is capable of making continuous gas-exchange measurements of
multiple species over a broad range of experimental conditions. This
system is validated by using a quantitative methanol-burning lung model
modified to provide reproducible 13CO2
production. The average error for
O2 and
CO2 over the FIO2 range of 0.21-0.8. is 2.4 and
0.8%, respectively. The instrument is capable of determining the
differential atom% volume of known references of
13CO2 to within 3.4%. This device reduces the
sources of error that thwart other instruments at
FIO2 > 0.40 and demonstrates the
capacity to explore other expressions of metabolic activity in exhaled gases related to the excretion of 13CO2.
oxygen consumption; carbon dioxide production; 13CO2; metabolic cart; indirect calorimetry; expired gas analysis; mass spectrometer; Douglas bag
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INTRODUCTION |
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QUANTITATIVE
GAS-EXCHANGE analysis remains one of the more difficult and
challenging physiological measurements. Conventional instrumentation is
confined to the measurements of oxygen consumption (
O2) and carbon dioxide production
(
CO2) and performs poorly in high-oxygen
environments (2, 5, 6,
9, 13, 16, 19).
These limitations restrict its applicability. Additionally, indirect
calorimetry only reveals a small part of the metabolic process. Some
advances in the study of metabolism necessitate the ability to quantify
other expired gases (i.e., 13CO2) to explore
pathways in organ function (8, 10,
14, 15, 17).
Cumbersome and generally limited to its comparison with other techniques, the Douglas bag technique has demonstrated the potential for greater accuracy than conventional systems and offers the opportunity to study the entire expired gas volume of innumerable species (3, 4, 12). We sought to devise an instrument capable of 1) improving the accuracy of conventional gas-exchange measurements over a broader range of clinical conditions, 2) providing the flexibility to study other aspects of metabolism related to the measurement of 13CO2, and 3) using Douglas bag methodology to provide a system of automated gas-exchange analysis (SAGE).
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MATERIALS AND METHODS |
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Two 60-liter vinyl nondiffusing gas-collection bags (no. 22619, Warren E. Collins, Braintree, MA) are suspended from a valve manifold
and mounted within a 66 cm × 66 cm × 108 cm (width × depth × height) movable enclosure (Fig.
1). The gas-collection bags are modified
with the addition of four gas ports near the corners of each bag. A
pump (model VP0660, Medo USA, Hanover Park, IL) with a nominal flow
rate of 25 l/min is used in conjunction with each Douglas bag's
supplemental ports to implement the recirculation manifold (Fig.
2). This manifold mixes gases within
11 s, ensuring concentration uniformity throughout the bag before
mass spectrometer sampling. To prevent condensation, the enclosure is
heated to ~41°C. Circulation fans ensure uniform temperature
distribution inside the enclosure. The gas-collection manifold is
formed from 25-mm-ID polyvinyl chloride plumbing stock and associated
fittings (elbows, T fittings, threaded adaptors). Large-bore (25-mm)
solenoid valves (model NGB7B, Alcan Valves, Itasca, IL), labeled
V1-V5, direct collected gas into the bags
or to an evacuation fan. Valve V2 acts as a bypass valve,
venting the subject's exhalation to room air when there is no
collection activity. A quadrupole mass spectrometer (RAMS-200,
Marquette Medical Systems, Milwaukee, WI) programmed to measure
O2, N2, 12CO2,
13CO2, Ar, and SF6 is used for gas
analysis. It is configured to discriminate between atomic mass
units 44 (12CO2) and 45 (13CO2) with sufficient resolution and
sensitivity to perform ratio measurements. Small valves,
V9-V11 (Clippard EVO-3, Cincinnati, OH)
route gas samples to the mass spectrometer from either the inspired gas
or the Douglas bag contents. The gas is analyzed for 4 s,
providing the average of 200 measurements for use by the system's
equations (see Table 1). This device is
portable and requires only 15 min of warm-up time to achieve its
specified accuracy. Physical measurements, analog-to-digital
conversions, valve actuation and sequencing, and communications with
the RAMS-200 mass spectrometer are under control of a printer port
computer interface (LPTek, Westbury, NY) and a standard personal
computer.
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An indicator-dilution gas system employing sulfur hexafluoride (SF6) is used to determine the volume of gases collected in each bag. SF6 (99.96%), from a supply tank located in the enclosure, pressurizes a steel dosing tank of known volume (1,590 ml) via valve V8. The dosing tank is packed with copper wool to ensure rapid temperature equilibration. An absolute pressure transducer (142PC30A, Honeywell Microswitch Div., Freeport, IL) is used to determine the dosing tank pressure. During operation, the dosing tank is pressurized to ~1.5 atm as measured by the absolute pressure transducer. Valve V6 or V7 routes the pressurized SF6 to either bag 1 or bag 2 via a centrally located port. By measuring the absolute ambient and tank pressures, and the tank and Douglas bag temperatures, it is possible to deliver a highly accurate volume of SF6 into the Douglas bags. A typical SF6 dose volume is ~750 ml. Cylinders containing 4.5 kg of SF6, which liquefies at >2,068 kPa, provide sufficient indicator gas for ~900 measurements. The dilution of SF6 in the Douglas bag is measured after dosing and again after collection to calculate the residual and total volumes, respectively.
The functional operations of the system are priming, evacuation, dosing, gas collection, analysis, and evacuation. These are interleaved between the two Douglas bags to permit continuous gas-exchange measurement. The total time required to perform one cycle of all functions is ~115 s/bag. The system is, therefore, programmed for a nominal 2-min collection interval with gas volumes reported in milliliters per minute. Under software control, alterations of the collection intervals can be made. The interconnection between the instrument and the subject consists of a face mask or a mouthpiece and nose clip and a set of nonrebreathing valves coupled to the front panel connector with a length of ventilator or pulmonary function tubing. A continuous flow hood could also be used. The exhalation port of a mechanical ventilator can be accessed to provide expired gas for collection.
Validation
Part 1.
The system was validated by using a modified version of the
quantitative funnel burner lung model of Miodownik et al.
(7). The modification substituted a water jacket for the
open pool of water used for cooling. This validation
technique is rigorous and generates precise, adjustable
O2 and
CO2 while simultaneously producing
saturated water vapor gas. Consequently, it closely reflects the
clinical environment encountered during measurement on spontaneously
breathing and mechanically ventilated patients. In addition, the
accuracy and precision of the SAGE total volume accumulation
measurement between 7 and 25 liters were tested by using standard water displacement.
O2 rate of 277 ml/min with a
corresponding
CO2
(12CO2 + 13CO2) of
185 ml/min (respiratory quotient = 0.667). The actual fuel
infusion rate was determined gravimetrically, and the measured rate was
translated into the expected
O2 and
CO2 and shown in Table
2. The measured methanol infusion rate
was 20.23 ml/h resulting in
O2 and
CO2 equal to 280 and 186 ml/min,
respectively. Twenty-six measurements were done at each
FIO2.
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Part 2. The accuracy of the SAGE was compared with that of the SensorMedics Deltatrac (Yorba Linda, CA) and the MedGraphics CPX (St. Paul, MN) gas-exchange instruments. These devices are representative of mixing-box and breath-by-breath techniques, respectively. Following manufacturer-specified calibration, these instrument were subjected to the validation protocol outlined in Part 1.
Part 3. The validation technique was expanded to test the ability of the SAGE to quantify small differences in 13CO2 concentration in volumes of gas collected over time. This process simulated the collection of 13CO2-enriched gas that results from the metabolism of 13C-enriched hydrocarbons. The abundance ratios of 13C to 12C (13C/12C; 1.0581 atom%) in both the batch of methanol burned and a tank of 100% CO2 (1.10532 atom%) were verified by mass ratio spectrometry (Metabolic Solutions, Nashua, NH) and provided, respectively, reference and measurement values for the simultaneous validation of 13CO2 production and 13C/12C enrichment. Methanol infused at 20 ml/h was burned for 2 h in the validation lung model to establish a baseline 13CO2 production. The lung model was ventilated at a nominal 10 l/min with room air. After this baseline collection, the flame was extinguished, and the tanked CO2 (abundance ratios of 13C/12C 1.0581 atom%) was introduced into the outlet of the lung model at a comparable rate (~185 ml/min) and collected by the SAGE for 2 h. The atom% difference between the 13CO2 produced by burning methanol and the 13CO2 of the tank provided a predetermined enrichment level. This was calculated to produce ~6 ml of enriched 13CO2 over the collection interval. This quantity of enriched 13CO2 is comparable to the expected recovery observed in 13C-labeled studies (14).
Statistics
The error (%) was defined as the difference between the actual measurement and the reference divided by the reference. The precision is the reproducibility of a measurement and is the SD expressed as percentage of the observed mean of
O2
and
CO2 (19). Table 2 lists
results as error with parenthetical precision values. Comparison of the
error and the precision between instruments was performed by using
ANOVA for repeated measures; t-tests were performed when necessary.
The atom% difference between the two sources of 13CO2 was evaluated by t-test. The results were expressed as means ± SD. The difference between the 13CO2 atom% in tanked gas at each time collection and the mean of the 13CO2 atom% of the reference methanol burn was calculated to generate a 13CO2 enrichment volume for each bag collection of tank gas. The 2-h collection was calculated as the sum of 13CO2 enrichment volume collected over 2 h. This value was compared with the calculated control from the known standard volumes and atom% of the test gas mixtures.
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RESULTS |
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The results of
O2 and
CO2 at each set of experimental
conditions for the SAGE, the SensorMedics Deltatrac, and the
MedGraphics CPX are shown in Table 2. All data are expressed as mean
error% with precision given in parentheses. The SAGE measured expired gas volume with a mean error of 1.1% (0.9%). The average
O2 error of the SAGE over
FIO2 of 0.21-0.80 was
2.4% (3.7).
The average
CO2 error over this range
was 0.8% (1.5). The SAGE
O2 error% was
significantly lower than the other units at
FIO2 > 0.40. The SensorMedics
Deltatrac average
O2 and
CO2 error was 11.4% (3.7) and 2.1%
(0.9), respectively, over the range of FIO2
studied. The MedGraphics CPX average
O2
and
CO2 error was 2.6% (4.5) and 1.7%
(2.7), respectively, over a narrower FIO2 range. The CPX was not tested at FIO2 > 0.60 because of manufacturer assertion of lack of accuracy at that
range. The Deltatrac and the CPX devices both exhibited increasing
O2 errors as
FIO2 was elevated. There was no difference
in
CO2 accuracy between instruments.
CO2 readings for all devices were
largely unaffected by FIO2.
The 13CO2/12CO2 atom%
measurements for the burning methanol and for the tanked
CO2, respectively, were 9.6 × 10
3 ± 2.0 × 10
4 and 1.0 × 10
2 ± 1.7 × 10
4. The differential atom% between the
two 13CO2 gases was measured at 4.8 × 10
4 with an error of +4.2% compared with the expected
differential. The 2-h collection of 13CO2
enrichment volume was 6.4 ml with an error of +3.4% compared with the
predicted 2-h collection.
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DISCUSSION |
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As an indirect calorimeter, the average
O2 error of the SAGE was significantly
less than the respective error for the Deltatrac and the CPX at
FIO2 > 0.40. At lower
FIO2, all three systems exhibited errors
that were not significantly different from each other. The measurement
of a varying gas flow is difficult and prone to multiple sources of
error. The increasing inaccuracy of the Deltatrac and the CPX can be
traced to the limitations of their flow-measuring devices. Because
there is no correction of pneumotachometer flow signal for
FIO2, temperature, and CO2
concentration, it is important to calibrate the instrument under
conditions close to those prevailing during testing. Both instruments
are initially and only calibrated at room air without correction for
ventilation of gases at higher FIO2. The
expired volume of water vapor must also be carefully accounted for
(22). Additional sources of error include the measurement
of dynamically changing gas concentrations and their proper alignment
with the flow signal over an acceptable frequency response range. Some
of these systems can yield
O2 errors
approaching 50-100 ml/min at elevated
FIO2 (1, 18).
The literature continues to compare the accuracy of modern gas-exchange techniques to the Douglas bag method (2-6, 9, 12, 13, 16, 19). The gas-collection bag contains the true mixed expired volume of gas expressed during the collection interval, independent of the flow pattern of the gas entering the bag, its collection site, or the activity of the subject. This is a major and obvious advantage noted by Douglas (4). The major factors that have made this technique cumbersome are ensuring thorough mixture of collected gas, determining the volume collected, withdrawing gas samples for analysis, and emptying the bags in preparation for their next use. To determine volume, the Douglas bag is often displaced into a spirometer (e.g., Tissot or gas meter) with corrections made for water vapor content (20). The literature refers to some of the problems in managing leaks, contamination with unwanted gases during bag manipulation, and other measurement errors during hyperoxic states (3). These functions have, traditionally, been done by hand. Although multiple bags can be collected and labeled for subsequent analysis, continuous measurement is unrealistic.
Our implementation of the SAGE addresses a number of the error sources associated with conventional gas exchange techniques and with manual Douglas bag methods. They are avoided by employing the two-bag automated collection system shown schematically in Fig. 1. By automatically interleaving, filling, analyzing, and emptying the Douglas bags contained within our instrument, a virtual infinite set of empty bags is made available, thus allowing continuous gas exchange measurement. The gas circulation system for each bag described in MATERIALS AND METHODS ensures rapid gas concentration equilibration before gas measurement. The SF6 indicator gas dilution permits automation of the volumetric measurement and eliminates the need for the error-prone measurement of flow to determine volume. In the context of a 2-min collection cycle, SAGE measurements are performed on static volumes having stable gas concentrations at each stage of the collection process, allowing accurate gas concentration measurements. Advantage can be taken of this static situation to significantly reduce errors by averaging several hundred individual physical determinations.
The mass spectrometer automatically normalizes the sum of all of the
gas species selected for measurement to 1.00. Since water vapor is not
selected as a measured gas, its volume is disregarded as a component of
normalization. Consequently, when the SF6 indicator is
diluted to determine bag volume, the component representing water vapor
is conveniently ignored. Through automation, opportunities for leaks
and contamination are minimized, and human error is eliminated. Our
results indicate that the SAGE
O2 error
increases to 5.8% at an FIO2 of 0.8. This
is a result of the N2 concentration measurement
accuracy required by the Haldane transformation as the
FIO2 is increased and the
accuracy limitation of the RAMS-200 mass spectrometer
(21). However, the SAGE is not particularly limited or
intimately tied to the RAMS-200 mass spectrometer. Indeed, we fully
anticipate making use of advances in mass spectrometry and gas analysis
instrumentation as they become available. The indicator dosing system
is not constrained to SF6 gas. The instrument is usable
with virtually any indicator gas that is accurately determined by the
gas measuring system.
The SAGE is restricted by the maximum gas volume that can accumulate during the collection interval (~60 liters). Although this system cannot respond to instantaneous changes in gas exchange, the 2-min cycle time for each bag collection is still short enough to allow observation of many dynamic events. This is comparable to the operation of both mixing-box and breath-by-breath instruments. The large volume associated with mixing chambers, i.e., Deltatrac, can reduce the resolution of the minute-by-minute measurements and yield substantially slower moving averages (1). Some breath-by-breath instruments, i.e., CPX, provide a moving average of eight or more breaths, obscuring instantaneous changes.
Having a true mixed expirate permits the expansion of metabolic gas
exchange to include species other than O2 and
CO2. It offers the intriguing possibility of investigating
aspects of metabolism via gas exchange in addition to via indirect
calorimetry. The 13CO2 validation test
demonstrates the ability of the SAGE to measure the
13CO2 component of CO2 with
sufficient accuracy to identify changes in the
13C/12C enrichment ratio and the excreted
volume of enriched 13CO2. The ability to
discriminate between small differences in atom% of
13CO2 allows the determination of enrichment
volume. This system permits analysis of expressions of metabolic
activity that are traceable to the conversion of
13C-labeled substrate to 13CO2 such
as gastrointestinal absorption; fat, carbohydrate, and protein
metabolism; and liver function (8, 10,
14, 15, 17). After
administration of the labeled metabolite, the excretion of expired
13CO2 is quantitated by collecting numerous
aliquots for later gas study. This process, time consuming and fraught
with errors, marginally approximates the excretion curve. Conventional
13C-labeled breath tests often approximate subjects'
CO2 production on the basis of either body weight (9 mmol · kg
1 · h
1) or body
surface area (5 mmol · m
2 · min
1). Such crude estimates of
CO2 are a significant source of
calculation error (14). The aliquot system is costly and
time consuming, and it fails to provide a complete portrait of
excretion. Without the assumptions inherent in the conventional
sampled-aliquot technique, the SAGE can offer a more accurate and
inexpensive alternative for 13CO2-substrate
breath tests. This application could provide sequential collections of
exhaled gas in a quantitative time course.
In conclusion, we have developed a new automated gas-exchange measurement instrument based on the Douglas bag method. The SAGE can reduce errors at high FIO2. We have demonstrated the ability to quantify small volumes of enriched 13CO2. The ability to perform continuous, unattended, quantitative analysis of expired gas could permit the study of the dynamics of metabolism over a multitude of conditions within a markedly reduced time frame.
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FOOTNOTES |
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Address for reprint requests and other correspondence: J. A. Melendez, Dept. of Anesthesiology and Critical Care Medicine, Memorial Sloan-Kettering Cancer Center, 1275 York Ave., New York, NY 10021 (E-mail: melendej{at}mskcc.org).
The costs of publication of this article were defrayed in part by the payment of page charges. The article must therefore be hereby marked "advertisement" in accordance with 18 U.S.C. §1734 solely to indicate this fact.
Received 9 October 1998; accepted in final form 17 March 2000.
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