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CN101000278A - Method and device for measuring pollutant discharging total of motor vehicle - Google Patents

Method and device for measuring pollutant discharging total of motor vehicle Download PDF

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Publication number
CN101000278A
CN101000278A CN 200710051254 CN200710051254A CN101000278A CN 101000278 A CN101000278 A CN 101000278A CN 200710051254 CN200710051254 CN 200710051254 CN 200710051254 A CN200710051254 A CN 200710051254A CN 101000278 A CN101000278 A CN 101000278A
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tail gas
gas
motor vehicle
dilution
flow
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熊友辉
刘志强
蒋泰毅
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WUHAN CUBIC OPTOELECTRONICS CO Ltd
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WUHAN CUBIC OPTOELECTRONICS CO Ltd
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Abstract

The invention relates to vehicle pollutant discharging total measuring device and method. The device is made up of diluting sampling tube, fan, computer measure-control system, chassis power measuring machine, fan flow rate adjusting device, flow rate, temperature, and pressure measuring devices, five components tail gas, O2, CO2 gas analysis devices. The measuring method includes the following steps: using fan flow rate adjusting device to control pumping drainage fan, measure diluted tail gas flow rate, temperature, pressure, O2, CO2 volume density; using five components gas analysis device to measure undiluted tail gas for each gas volume density; calculating out the undiluted tail gas flow rate by the volume density ratio to gain vehicle pollutants discharging gross. The invention has high detecting precision for tail gas, can be used in pollutants discharging gross detecting for vehicle operating condition method tail gas detecting line or repair shop.

Description

A kind of measurement mechanism of pollutant discharging total of motor vehicle and method
Technical field
The present invention relates to a kind of measurement mechanism and method of pollutant discharging total of motor vehicle.
Background technology
Along with automobile volume of production and marketing in recent years increases progressively fast, the generation of a large amount of automotive emissions has become a pervasive social problem, and some urban automobile exhaust emission has become first pollution source, city.Existing automobile exhaust pollutant discharge amount detection method has FTP, ASM and IM240 method.The ASM detection method owes just and sound based on pollutant emission concentration rather than total emission volumn to the vehicle of different engine displacement, and can't carry out total amount of pollutant statistics; The IM240 method is very little with respect to FTP result's discreteness to the test result of HC, CO, three kinds of pollutants of NO, and false determination ratio is very low, but IM240 operating condition method cost of equipment is relatively more expensive, and day-to-day operation is safeguarded more complicated, is difficult to large tracts of land and promotes.In order to overcome the difficulty that ASM and FTP correlativity are poor, the IM240 expense is too high and be unfavorable for promoting, the detection method of existing IG240 (VMAS), this method relevant technologies core can be with reference to U.S. Patent number: US6387706 and US6085582 (VEHICLE MASS EMISSION MEASUREMENT).Domestic also have enterprise to propose based on CO on this patent basis 2The patent of spike " a kind of measurement mechanism of motor vehicle emission pollutant total amount and method thereof " (number of patent application CN200410051631.2), above patented method substantial principle is the same: comprise dilution collection flexible pipe, blower fan, a dilution exhaust flow measurement mechanism of collecting tail gas and air, first gas analysis module that five component gas that meet the BAR97 standard of the tail gas of a measurement not diluted are analyzed, an O who measures diluents 2Perhaps CO 2Second gas analysis module of concentration is by O in two analysis modules 2Perhaps CO 2Concentration calculates the dilution ratio of dilution tail gas, and calculates the exhaust flow of not diluted, thereby obtains the mass rate of tail gas.But its flow that extracts dilution tail gas is (being about 120L/s) fixed, motor vehicle for different displacements, dilution ratio alters a great deal, when extraction flow during at 120L/s, 2.4L the dilution ratio of the motor vehicle of discharge capacity when idling is about 3%, its dilution ratio of the motor vehicle of 0.8L discharge capacity has only about 1%.O as tracer gas 2Perhaps CO 2Concentration change is very little, and minimum error is (as O 2When error is absolute percent content 0.1%, CO 2When error is absolute percent content 0.04%) may cause the error of dilution ratio of calculating very big.In addition, foreign patent adopts zirconium oxide oxygen sensor as tracing method to dilution tail gas, but the tail gas oxygen detection of not diluted adopts electrochemical sensor, and both differ greatly the response time, is difficult to realize transient response.And the CO in the dilution tail gas, HC are very big to the zirconium oxide oxygen sensor influence, cause than mistake easily.Domestic employing CO 2Though the method for spike has solved the problem of transient response, CO 2Spike causes bigger dilution ratio error easily, and this is also by domestic a large amount of evidence.More than the analysis showed that: previous methods is not suitable for the measurement of the motor-vehicle tail-gas of a large amount of 0.8L-1.8L discharge capacities of China, can't satisfy China simultaneously in the requirement with the car simple transient behavior method yet.So domestic urgent need a kind of novel pollutant discharging total of motor vehicle proving installation and method.
Summary of the invention
Purpose of the present invention aims to provide a kind of can the adjustment automatically according to detected motor car engine displacement size and dilutes tail gas pump drainage flow, and measures flow, temperature, pressure, the O of dilution tail gas 2Volumetric concentration, CO 2Volumetric concentration; Adopt CO, HC, CO in the tail gas of five component tails assay measurement device not diluted simultaneously 2, NO and O 2Volumetric concentration, the O in tail gas by not diluted and the dilution tail gas 2, CO 2Volumetric concentration ratio, adopt O 2, CO 2Two kinds of gas calculates not diluted as tracer gas tail gas in dilution tail gas dilution ratio and obtain the exhaust flow of not diluted, and then obtain pollutant discharging total of motor vehicle, measurement mechanism and the method high to the tail gas accuracy of detection.
The implementation of the object of the invention is, a kind of measurement mechanism of pollutant discharging total of motor vehicle, the gas outlet that connects tested motor vehicle with bell-mouthed dilution sampling pipe 2 inlets, outlet is connected to blower fan 3, the blower fan 3 machine flow regulator 4 of giving a dinner for a visitor from afar, the control interface of computer measurement and control system 9 connects chassis dynamometer 1 and compressor flow regulating device 4, flow, temperature, device for pressure measurement 5, five component tails assay devices 6, O 2Gas analyzing apparatus 7, CO 2The interface of gas analyzing apparatus 8 connects computer measurement and control system 9.Sampling probe 10 output terminals connect five component tails assay devices 6, and input end is positioned at the gas outlet of motor vehicle.
A kind of measuring method of pollutant discharging total of motor vehicle, carry out according to the following steps:
1) CO 2Gas analyzing apparatus 8 extracts through CO 2The filtrator filtered air returns to zero, CO 2Be 0, O 2Gas analyzing apparatus 7 returns to zero O by draw ambient air 2Be that 20.90%, five component tails assay device 6 returns to zero by extracting the surrounding air that filters through HC, CO, HC, NO are 0, CO 2Be 0.04, O 2Be 20.90%,
2) will be with the hydraucone of bell-mouthed dilution sampling pipe 2 the gas outlet mouth of pipe over against tested motor vehicle, extract the air of whole exhausts of motor vehicle and participation dilution by blower fan 3, and with the dilution tail gas be transported to flow, temperature, device for pressure measurement 5, the sampling probe 10 of five component tails assay devices 6 inserts in the tested motor vehicle exhaust, directly extract the tail gas of not diluted
3) computer measurement and control system 9 is by the extraction flow of compressor flow regulating device 4 control blower fans 3, makes when motor vehicle during at idling mode CO 2The CO that gas analyzing apparatus 8 and five component tails assay devices 6 obtain respectively 2Volumetric concentration compares between 3%~5%,
4) computer measurement and control system 9 control chassis dynamometers 1 load, and chassis dynamometer 1 is with motor vehicle real-time speed V iSend to computer measurement and control system 9,
5) flow, temperature, device for pressure measurement 5 are measured flow Q, temperature T, the pressure P of dilution tail gas, O 2Gas analyzing apparatus 7, CO 2Gas analyzing apparatus 8 is measured the O in the dilution tail gas respectively 2Volumetric concentration D O2And CO 2Volumetric concentration D CO2, and above signal sent to computer measurement and control system 9 by interface,
6) five component tails assay devices 6 pass through to insert the sampling probe 10 of motor vehicle exhaust with normal flow Q eExtract the tail gas of not diluted, and measure CO, HC, CO in the tail gas of not diluted in real time 2, NO, O 2Volumetric concentration C i, and signal sent to computer measurement and control system 9 by interface,
7) computer measurement and control system 9 is according to five component tails assay devices 6 and flow, temperature, device for pressure measurement, O 2Gas analyzing apparatus 7, CO 2The signal that gas analyzing apparatus 8 sends over carries out data processing, obtains the flow Q of the dilution tail gas under the standard state s, by five component tails assay devices 6, O 2Gas analyzing apparatus 7, CO 2Gas analyzing apparatus 8 obtains the CO of the tail gas of not diluted respectively 2Volumetric concentration R CO2, O 2Volumetric concentration R O2, the dilution tail gas CO 2Volumetric concentration D CO2And O 2Volumetric concentration D O2, calculate the dilution ratio R of dilution tail gas, and calculate the normal flow Qss of the tail gas of not diluted, obtain CO, HC, CO in the tail gas of not diluted by five component tails assay devices 6 2, NO real-time volumetric concentration Ci, the normal flow Qss in conjunction with the tail gas of not diluted obtains CO, HC, CO 2, the NO unit interval mass M i, and then obtain total discharging M of pollutant Total, the real-time speed V that chassis dynamometer 1 is sended over iAdd up obtain motor-driven vehicle going apart from d, calculate the every km pollutant discharge amount of motor vehicle M at last.
The present invention is owing to adopted the automatic flow regulating device, and having overcome in the past fixedly, the pump drainage flow is not suitable for the measurement of domestic automobile with small output volume, single employing O 2Perhaps CO 2The low shortcoming of dilution ratio measuring accuracy is calculated in spike, has adopted extraction flow to adjust automatically and O 2, CO 2Two kinds of tracer gas techniques calculate the technology of dilution ratio, make a covering device can be fit to measure all vehicles that discharge capacity is 0.8L-6.0L, to tail gas accuracy of detection height, be fit to the requirement of transient response more, improved the accuracy of test, provide a kind of new device for China's vehicle operating condition method tail gas detects.
Description of drawings
Fig. 1 is a measurement mechanism structural representation of the present invention
Fig. 2 is the process flow diagram of measuring method of the present invention
Embodiment
With reference to Fig. 1, the gas outlet that connects tested motor vehicle with bell-mouthed dilution sampling pipe 2 inlets, outlet is connected to blower fan 3, the blower fan 3 machine flow regulator 4 of giving a dinner for a visitor from afar, the control interface of computer measurement and control system 9 connects chassis dynamometer 1 and compressor flow regulating device 4, flow, temperature, device for pressure measurement 5, five component tails assay devices 6, O 2Gas analyzing apparatus 7, CO 2The interface of gas analyzing apparatus 8 connects computer measurement and control system 9.Sampling probe 10 output terminals connect five component tails assay devices 6, and input end is positioned at the gas outlet of motor vehicle.
O 2Gas analyzing apparatus 7, CO 2Gas analyzing apparatus 8 is directly measured the O in the dilution tail gas from being positioned at the rear end sample tap sampling of flow, temperature, device for pressure measurement 5 2, CO 2Volumetric concentration.Five component tails assay devices 6 insert in the tested motor vehicle exhaust by sampling probe 10, directly extract the tail gas of not diluted, analyze CO, HC, CO in the tail gas 2, NO, O 2Volumetric concentration.
At the tested vehicle of different displacements, the present invention is by the flow of compressor flow regulating device 4 control blower fans 3, makes the vehicle of various discharge capacities when idling, CO 2CO in the dilution tail gas that gas analyzing apparatus 8 records 2CO in the tail gas of the not diluted that volumetric concentration and five component tails assay devices 6 record 2Volumetric concentration ratio is unlikely to cause the phenomenon that rare excessively, the big discharge capacity car of tail gas dilutes tail gas overrich in the tail gas in the automobile with small output volume dilution tail gas between 3%~5%.Tail gas after the dilution is by being with bell-mouthed dilution sampling pipe 2 and flow, temperature, device for pressure measurement 5, O 2Gas analyzing apparatus 7, CO 2Behind the gas analyzing apparatus 8 measuring-signal is sent to computer measurement and control system 7, five component tails assay devices 6 and analyze by sampling probe 10 directly extracts not diluted from tested motor vehicle exhaust tail gas, and with CO, HC, CO 2, NO, O 2The volumetric concentration signal send to computer measurement and control system 7.Computer measurement and control system 7 calculates normal flow, the dilution ratio of dilution tail gas, the exhaust flow of not diluted automatically, and according to the exhaust flow and the gas volumetric concentration of not diluted, the total amount of robot brain motor-car pollutant emission.
Compressor flow regulating device 4 can be electronically controlled frequency converter or electronically controlled transformer.Adopt the flow of electronically controlled frequency converter or electronically controlled transformer control blower fan to belong to known technology.Flow, temperature, device for pressure measurement 5, five component tails assay devices 6, O 2Gas analyzing apparatus 7, CO 2The flow sensor that gas analyzing apparatus 8 needs, temperature sensor, pressure transducer, NDIR infrared gas sensor, electrochemical gas sensor, zirconium oxide oxygen sensor and the electrical signal conversion mechanism that needs all belong to the measuring equipment in the known technology.The interface of chassis dynamometer 1, compressor flow regulating device 4, flow, temperature, device for pressure measurement 5, five component tails assay devices 6, O2 gas analyzing apparatus 7, CO2 gas analyzing apparatus 8 and computer measurement and control system 9, can be interfaces such as RS232, RS485, also can adopt interfaces such as A/D, D/A data acquisition control card, these all belong to known technology.
With reference to Fig. 2, measuring method of the present invention is: CO 2Gas analyzing apparatus 8 extracts through CO 2Filtrator filtered air (the CO that returns to zero 2Be 0), O 2Gas analyzing apparatus 7 is by the draw ambient air (O that returns to zero 2Be 20.90%), five component tails assay devices 6 return to zero by the surrounding air that extracts process HC filtration, and (CO, HC, NO are 0, CO 2Be 0.04, O 2Be 20.90%), with the hydraucone of dilution sampling pipe the gas outlet mouth of pipe over against tested motor vehicle, extract the air of whole exhausts of motor vehicle and participation dilution by blower fan 3, and with the dilution tail gas be transported to flow, temperature, device for pressure measurement 5, computer measurement and control system 9 is by the extraction flow of compressor flow regulating device 4 control blower fans 3, make when motor vehicle during CO at idling mode 2CO in the dilution tail gas that gas analyzing apparatus 8 records 2CO in the tail gas of the not diluted that volumetric concentration and five component tails assay devices 6 record 2Volumetric concentration ratio is between 3%~5%, and according to the testing standard requirement, control chassis measurement of power 1 machine loads, and reads real-time traffic Q, temperature T, pressure P, the O of dilution tail gas 2Volumetric concentration, CO 2CO, HC, CO in the tail gas of volumetric concentration and not diluted 2, NO, O 2Volumetric concentration C i, calculate real-time dilution ratio R and by second calculating CO, a HC, CO 2, NO the mass M of unit interval i, according to real-time speed V iCalculate operating range d, after the end of test (EOT), calculate total discharging M Total, total operating range d and every km pollutant discharge amount M.
Concrete computing method are as follows:
The flow Qs (L/s) of the dilution tail gas under the standard state calculates by following formula:
Q S = Q × P T × T 0 P 0
In the formula:
The flow L/s that flow sensor records in Q---flow, temperature, the device for pressure measurement,
The pressure kPa that pressure transducer records in P---flow, temperature, the device for pressure measurement,
The temperature K that temperature sensor records in T---flow, temperature, the device for pressure measurement,
P 0---the pressure under the standard state, 101.325kPa,
T 0---the temperature under the standard state, 273.15K.
The normal flow Qss of the dilution ratio R of dilution tail gas and the tail gas of not diluted calculates by following formula:
R 1 = D CO 2 R CO 2
D CO=R CO×R 1
D HC=R HC×R 1
T O2=D O2+D CO(a+b×D CO)+D HC(c+d×D HC)
R 2 = 20.9 - T O 2 20.9 - R O 2
R = R 1 + R 2 2
Q ss=Q s×R+Q e
In the formula:
R 1---pass through CO 2The dilution ratio that spike is calculated,
P 2---pass through O 2The dilution ratio that spike is calculated,
D CO2---pass through CO 2CO in the dilution tail gas that gas analyzing apparatus is measured 2Content,
DO 2---pass through O 2O in the dilution tail gas that gas analyzing apparatus is measured 2Content,
D CO---pass through R 1CO content in the dilution tail gas of calculating,
D HC---pass through R 1HC content in the dilution tail gas of calculating,
T O2---by the O in the dilution tail gas that calculates 2Content,
R O2---the O in the tail gas of the not diluted by five component tails assay measurement devices 2Content,
R CO2---the CO in the tail gas of the not diluted by five component tails assay measurement devices 2Content,
R CO---the CO content in the tail gas of the not diluted by five component tails assay measurement devices,
R HC---the HC content in the tail gas of the not diluted by five component tails assay measurement devices,
Q e---the normal flow of the tail gas of the not diluted that five component tails assay devices extract,
A, b, c, d---correction factor is for diluting HC in the tail gas, CO volumetric concentration to adopting O 2The O that gas analyzing apparatus records 2The correction factor of the influence of volumetric concentration.
Below enumerate one and calculate correction factor a, b, c, the example of d:
Toward O 2Feed in the gas analyzing apparatus and comprise CO, HC, O 2, concentration is respectively D CO, D HC, T O2Mixed gas, O 2The reading of gas analyzing apparatus is D O2, obtain following table:
D HC (10 -6) D CO (10 -2) T O2 (10 -2) D O2 (10 -2)
1 0.000 0.000 20.900 20.900
2 148.200 0.000 19.860 19.690
3 296.400 0.000 18.810 18.580
4 444.600 0.000 17.820 17.540
5 592.800 0.000 16.820 16.470
6 742.000 0.000 15.730 15.390
7 889.200 0.000 14.630 14.300
8 0.000 .250 19.860 19.740
9 0.000 .500 18.810 18.590
10 0.000 .750 17.820 17.430
11 0.000 1.000 16.820 16.270
12 0.000 1.250 15.730 15.120
13 0.000 1.500 14.630 13.950
Therefore by experiment can be from O 2The reading D of gas analyzing apparatus O2And D CO, D HC, T O2O in the dilution tail gas that obtains obtaining by regression Calculation 2Content:
Regression equation:
T O2=D O2+D CO(a+b×D CO)+D HC(c+d×D HC)
Regression result: correction factor a, b, c, d is
a=0.5647,b=-0.0648,c=0.000996,d=-0.000001。
The mass M of the unit interval of HC, NO i(g/s) calculate by following formula:
M i = C i × 10 - 6 × Q ss × FZL K 1
In the formula:
C i---HC after the correction or the part per million volumetric concentration of NO,
The flow L/s of the dilution tail gas under Qss---the standard state,
The gram molecular weight of FZL---HC or NO is respectively 86g/mol and 30g/mol,
K 1---the gram molecular volume of ideal gas, 22.4136L/mol.
8, the measuring method of a kind of pollutant discharging total of motor vehicle according to claim 4 is characterized in that CO, CO 2The mass M of unit interval i(g/s) calculate by following formula:
M i = C i × 10 - 2 × Q ss × FZL K 1
In the formula:
C---CO or CO after the correction 2Percent volume concentration,
The flow of the dilution tail gas under Qss---the standard state, L/s,
FZL---CO or CO 2Gram molecular weight, be respectively 28g/mol and 44g/mol,
K 1---the gram molecular volume of ideal gas, 22.4136L/mol.
9, the measuring method of a kind of pollutant discharging total of motor vehicle according to claim 4 is characterized in that the total discharging M of motor vehicle at certain pollutant of 0-t in the time Total(g) calculate by following formula:
M total = Σ i = 0 t M i
In the formula:
M i---total discharge capacity g of certain pollutant of unit interval,
Calculating by following formula of interior motor-driven vehicle going of 0-t time apart from d (km):
d = Σ 0 t V i
In the formula:
V i---motor vehicle real-time speed km/s.
10, the measuring method of a kind of pollutant discharging total of motor vehicle according to claim 4 is characterized in that the every km pollutant discharge amount of motor vehicle M (g/km) calculates by following formula:
M = M total d
In the formula:
M Total---total discharge capacity g of certain pollutant in the 0-t time,
Motor-driven vehicle going apart from km in d---the 0-t time.

Claims (10)

1, a kind of measurement mechanism of pollutant discharging total of motor vehicle, it is characterized in that connecting the gas outlet of tested motor vehicle with bell-mouthed dilution sampling pipe (2) inlet, outlet is connected to blower fan (3), blower fan (3) the machine flow regulator (4) of giving a dinner for a visitor from afar, the control interface of computer measurement and control system (9) connects chassis dynamometer (1) and compressor flow regulating device (4), flow, temperature, device for pressure measurement (5), five component tails assay devices (6), O 2Gas analyzing apparatus (7), CO 2The interface of gas analyzing apparatus (8) connects computer measurement and control system (9).Sampling probe (10) output terminal connects five component tails assay devices (6), and input end is positioned at the gas outlet of motor vehicle.
2, the measurement mechanism of a kind of pollutant discharging total of motor vehicle according to claim 1 is characterized in that O 2Gas analyzing apparatus (7), CO 2Gas analyzing apparatus (8) is positioned at the rear end of flow, temperature, device for pressure measurement (5).
3, the measurement mechanism of a kind of pollutant discharging total of motor vehicle according to claim 1 is characterized in that compressor flow regulating device (4) is electronically controlled frequency converter or electronically controlled transformer.
4, a kind of measuring method of pollutant discharging total of motor vehicle is characterized in that carrying out according to the following steps:
1) CO 2Gas analyzing apparatus (8) extracts through CO 2The filtrator filtered air returns to zero, CO 2Be 0, O 2Gas analyzing apparatus (7) returns to zero O by draw ambient air 2Be that 20.90%, five component tails assay device (6) returns to zero by extracting the surrounding air that filters through HC, CO, HC, NO are 0, CO 2Be 0.04, O 2Be 20.90%,
2) will be with the hydraucone of bell-mouthed dilution sampling pipe (2) the gas outlet mouth of pipe over against tested motor vehicle, extract the air of whole exhausts of motor vehicle and participation dilution by blower fan (3), and with the dilution tail gas be transported to flow, temperature, device for pressure measurement (5), the sampling probe (10) of five component tails assay devices (6) inserts in the tested motor vehicle exhaust, directly extract the tail gas of not diluted
3) computer measurement and control system (9) is by the extraction flow of compressor flow regulating device (4) control blower fan (3), makes when motor vehicle during at idling mode CO 2The CO that gas analyzing apparatus (8) and five component tails assay devices (6) obtain respectively 2Volumetric concentration compares between 3%~5%,
4) computer measurement and control system (9) control chassis dynamometer (1) loads, and chassis dynamometer (1) is with motor vehicle real-time speed V iSend to computer measurement and control system (9),
5) flow, temperature, device for pressure measurement (5) are measured flow Q, temperature T, the pressure P of dilution tail gas, O 2Gas analyzing apparatus (7), CO 2Gas analyzing apparatus (8) is measured the O in the dilution tail gas respectively 2Volumetric concentration DO 2And CO 2Volumetric concentration D CO2, and above signal sent to computer measurement and control system (9) by interface,
6) five component tails assay devices (6) pass through to insert the sampling probe (10) of motor vehicle exhaust with normal flow Q eExtract the tail gas of not diluted, and measure CO, HC, CO in the tail gas of not diluted in real time 2, NO, O 2Volumetric concentration C i, and signal sent to computer measurement and control system (9) by interface,
7) computer measurement and control system (9) is according to five component tails assay devices (6) and flow, temperature, device for pressure measurement, O 2Gas analyzing apparatus (7), CO 2The signal that gas analyzing apparatus (8) sends over carries out data processing, obtains the flow Q of the dilution tail gas under the standard state s, by five component tails assay devices (6), O 2Gas analyzing apparatus (7), CO 2Gas analyzing apparatus (8) obtains the CO of the tail gas of not diluted respectively 2Volumetric concentration R CO2, O 2Volumetric concentration R O2, the dilution tail gas CO 2Volumetric concentration D CO2And O 2Volumetric concentration D O2, calculate the dilution ratio R of dilution tail gas, and calculate the normal flow Q of the tail gas of not diluted Ss, obtain CO, HC, CO in the tail gas of not diluted by five component tails assay devices (6) 2, NO real-time volumetric concentration Ci, in conjunction with the normal flow Q of the tail gas of not diluted Ss, obtain CO, HC, CO 2, the NO unit interval mass M i, and then obtain total discharging M of pollutant Total, the real-time speed V that chassis dynamometer (1) is sended over iAdd up obtain motor-driven vehicle going apart from d, calculate the every km pollutant discharge amount of motor vehicle M at last.
5, the measuring method of a kind of pollutant discharging total of motor vehicle according to claim 4 is characterized in that the flow Q of the dilution tail gas under the standard state s(L/s) calculate by following formula:
Q s = Q × P T × T 0 P 0
In the formula:
The flow L/s that flow sensor records in Q---amount, temperature, the device for pressure measurement,
The pressure kPa that pressure transducer records in P---amount, temperature, the device for pressure measurement,
The temperature K that temperature sensor records in T---amount, temperature, the device for pressure measurement,
P 0---the pressure under the accurate state, 101.325kPa,
T 0---the temperature under the accurate state, 273.15K.
6, the measuring method of a kind of pollutant discharging total of motor vehicle according to claim 4 is characterized in that diluting the normal flow Q of the tail gas of the dilution ratio R of tail gas and not diluted SsCalculate by following formula:
R 1 = D co 2 R co 2
D CO=R CO×R 1
D HC=R HC×R 1
T O2=D O2+D CO(a+b×D CO)+D HC(c+d×D HC)
R 2 = 20.9 - T O 2 20.9 - R O 2
R = R 1 + R 2 2
Q ss=Q s×R+Q e
In the formula:
R 1---pass through CO 2The dilution ratio that spike is calculated,
R 2---pass through O 2The dilution that spike is calculated,
D CO2---pass through CO 2CO in the dilution tail gas that gas analyzing apparatus is measured 2Content,
D O2---pass through O 2O in the dilution tail gas that gas analyzing apparatus is measured 2Content,
D CO---pass through R 1CO content in the dilution tail gas of calculating,
D HC---pass through R 1HC content in the dilution tail gas of calculating,
T O2---by the O in the dilution tail gas that calculates 2Content,
R O2---the O in the tail gas of the not diluted by five component tails assay measurement devices 2Content,
R CO2---the CO in the tail gas of the not diluted by five component tails assay measurement devices 2Content,
R CO---the CO content in the tail gas of the not diluted by five component tails assay measurement devices,
R HC---the HC content in the tail gas of the not diluted by five component tails assay measurement devices,
Q e---the normal flow of the tail gas of the not diluted that five component tails assay devices extract,
A, b, c, d---correction factor is for diluting HC in the tail gas, CO volumetric concentration to adopting O 2The O that gas analyzing apparatus records 2The correction factor of the influence of volumetric concentration.
7, the measuring method of a kind of pollutant discharging total of motor vehicle according to claim 4 is characterized in that the mass M of the unit interval of HC, NO i(g/s) calculate by following formula:
M i = C i × 10 - 6 × Q ss × FZL K 1
In the formula:
C i---HC after the correction or the part per million volumetric concentration of NO,
Q Ss---the flow L/s of the dilution tail gas under the standard state,
The gram molecular weight of FZL---HC or NO is respectively 86g/mol and 30g/mol,
K 1---the gram molecular volume of ideal gas, 22.4136L/mol.
8, the measuring method of a kind of pollutant discharging total of motor vehicle according to claim 4 is characterized in that CO, CO 2The mass M of unit interval i(g/s) calculate by following formula:
M i = C i × 10 - 2 × Q ss × FZL K 1
In the formula:
C---CO or CO after the correction 2Percent volume concentration,
Q Ss---the flow of the dilution tail gas under the standard state, L/s,
FZL---CO or CO 2Gram molecular weight, be respectively 28g/mol and 44g/mol,
K 1---the gram molecular volume of ideal gas, 22.4136L/mol.
9, the measuring method of a kind of pollutant discharging total of motor vehicle according to claim 4 is characterized in that the total discharging M of motor vehicle at certain pollutant of 0-t in the time Total(g) calculate by following formula:
M total = Σ i = 0 t M i
In the formula:
M i---total discharge capacity g of certain pollutant of unit interval,
Calculating by following formula of interior motor-driven vehicle going of 0-t time apart from d (km):
d = Σ 0 t V i
In the formula:
V i---motor vehicle real-time speed km/s.
10, the measuring method of a kind of pollutant discharging total of motor vehicle according to claim 4 is characterized in that the every km pollutant discharge amount of motor vehicle M (g/km) calculates by following formula:
M = M total d
In the formula:
M Total---total discharge capacity g of certain pollutant in the 0-t time,
Motor-driven vehicle going apart from km in d---the 0-t time.
CN 200710051254 2007-01-12 2007-01-12 Method and device for measuring pollutant discharging total of motor vehicle Pending CN101000278A (en)

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Cited By (24)

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CN102162772A (en) * 2010-12-24 2011-08-24 财团法人车辆研究测试中心 Device and the method for monitoring vehicle emissions
CN101382530B (en) * 2008-09-23 2012-10-10 佛山市南华仪器股份有限公司 Method for rapid measuring automobile exhaust pollutant by logic discrimination function
CN101387577B (en) * 2007-09-11 2013-06-19 通用汽车环球科技运作公司 Onboard trip computer for emissions subject to reduction credits
CN103234758A (en) * 2013-04-07 2013-08-07 浙江大学 Method and control device for simulating tail gas state of diesel engine
CN103308317A (en) * 2013-07-04 2013-09-18 交通运输部公路科学研究院 Liquid water drainage quantity testing device and method of automobile exhaust pipe
CN103543016A (en) * 2013-10-18 2014-01-29 联合汽车电子有限公司 Complete vehicle operating-mode exhaust gas emission testing system
CN103553082A (en) * 2013-10-14 2014-02-05 青海盐湖工业股份有限公司 On-line monitoring system of carnallite decomposition process and method thereof
CN103699058A (en) * 2012-05-24 2014-04-02 株式会社堀场制作所 Test system and device management apparatus
CN104412095A (en) * 2012-06-11 2015-03-11 Avl测试系统公司 Exhaust sampling system and method for synchronizing time alignment and dilation
CN104637115A (en) * 2014-12-25 2015-05-20 杨文俊 Working-condition-process tail gas detection line black box monitoring system with Bluetooth interface
CN104849068A (en) * 2015-05-25 2015-08-19 中国环境科学研究院 Heavy-duty vehicle rapid portable emission measurement system and method
CN105043780A (en) * 2015-06-11 2015-11-11 上海中船三井造船柴油机有限公司 Method for measuring nitrogen oxide emission of multi-turbocharger diesel
CN105277397A (en) * 2015-11-27 2016-01-27 堀场仪器(上海)有限公司 Vehicle tail gas collection device as well as vehicle tail gas detection system and method
CN105527383A (en) * 2016-01-13 2016-04-27 长春工程学院 Complex-environment multiple-working-condition automobile exhaust gas measuring method
CN106372806A (en) * 2016-09-12 2017-02-01 上海中船三井造船柴油机有限公司 Measurement method and apparatus used for CO2 gas discharge of ship diesel engine
CN106918637A (en) * 2017-04-14 2017-07-04 中国石油化工股份有限公司 The online total hydrocarbon concentration monitoring device and method of gas treatment equipment
CN106932207A (en) * 2017-03-17 2017-07-07 广州汽车集团股份有限公司 Vehicle discharge scaling method and the system of vehicle
CN108414033A (en) * 2017-01-19 2018-08-17 株式会社堀场制作所 Extraction flow determination unit and exhaust gas analyzer
CN108692995A (en) * 2018-05-16 2018-10-23 南通大学 The Portable diesel vehicle particle sampling device of commercial PM sampling instruments can be connected
CN108918204A (en) * 2018-05-16 2018-11-30 南通大学 The portable gasoline vehicle particle sampling device of commercial PM sampling instrument can be connected
CN109425492A (en) * 2017-08-22 2019-03-05 上海汽车集团股份有限公司 A kind of fixed device and its installation method
CN110987473A (en) * 2019-12-06 2020-04-10 辽宁龙马安泰网络技术有限责任公司 Distance correction method for transient fuel or waste gas of automobile bench test
CN112730308A (en) * 2021-01-04 2021-04-30 东风汽车股份有限公司 Device and method for testing tail gas components of whole vehicle
CN117407827A (en) * 2023-12-15 2024-01-16 湖南辉达净化工程有限公司 Abnormal operation data detection method for purification engineering waste gas purification equipment

Cited By (40)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101387577B (en) * 2007-09-11 2013-06-19 通用汽车环球科技运作公司 Onboard trip computer for emissions subject to reduction credits
CN101382530B (en) * 2008-09-23 2012-10-10 佛山市南华仪器股份有限公司 Method for rapid measuring automobile exhaust pollutant by logic discrimination function
CN102162772B (en) * 2010-12-24 2013-04-03 财团法人车辆研究测试中心 Device and the method for monitoring vehicle emissions
CN102162772A (en) * 2010-12-24 2011-08-24 财团法人车辆研究测试中心 Device and the method for monitoring vehicle emissions
CN103699058A (en) * 2012-05-24 2014-04-02 株式会社堀场制作所 Test system and device management apparatus
CN103699058B (en) * 2012-05-24 2017-08-25 株式会社堀场制作所 Test system and equipment management device
CN104412095A (en) * 2012-06-11 2015-03-11 Avl测试系统公司 Exhaust sampling system and method for synchronizing time alignment and dilation
CN104412095B (en) * 2012-06-11 2017-10-10 Avl测试系统公司 The tail gas sampling system and method for being aligned and expanding for lock in time
CN103234758B (en) * 2013-04-07 2015-11-11 浙江大学 The method of simulation diesel engine vent gas state and control device thereof
CN103234758A (en) * 2013-04-07 2013-08-07 浙江大学 Method and control device for simulating tail gas state of diesel engine
CN103308317A (en) * 2013-07-04 2013-09-18 交通运输部公路科学研究院 Liquid water drainage quantity testing device and method of automobile exhaust pipe
CN103553082A (en) * 2013-10-14 2014-02-05 青海盐湖工业股份有限公司 On-line monitoring system of carnallite decomposition process and method thereof
CN103553082B (en) * 2013-10-14 2015-08-12 青海盐湖工业股份有限公司 A kind of system and method for on-line monitoring carnallitite decomposition course
CN103543016A (en) * 2013-10-18 2014-01-29 联合汽车电子有限公司 Complete vehicle operating-mode exhaust gas emission testing system
CN103543016B (en) * 2013-10-18 2016-09-28 联合汽车电子有限公司 Car load condition tail gas system for testing discharge
CN104637115A (en) * 2014-12-25 2015-05-20 杨文俊 Working-condition-process tail gas detection line black box monitoring system with Bluetooth interface
CN104637115B (en) * 2014-12-25 2019-08-20 杨文俊 A kind of band blue tooth interface operating condition method tail gas detection line black box sub-monitoring system
CN104849068B (en) * 2015-05-25 2017-07-14 中国环境科学研究院 The quick on-board emission test method of heavy-duty car
CN104849068A (en) * 2015-05-25 2015-08-19 中国环境科学研究院 Heavy-duty vehicle rapid portable emission measurement system and method
CN105043780A (en) * 2015-06-11 2015-11-11 上海中船三井造船柴油机有限公司 Method for measuring nitrogen oxide emission of multi-turbocharger diesel
CN105043780B (en) * 2015-06-11 2017-10-31 上海中船三井造船柴油机有限公司 A kind of discharged nitrous oxides measuring method of many booster diesel engines
CN105277397A (en) * 2015-11-27 2016-01-27 堀场仪器(上海)有限公司 Vehicle tail gas collection device as well as vehicle tail gas detection system and method
CN105527383A (en) * 2016-01-13 2016-04-27 长春工程学院 Complex-environment multiple-working-condition automobile exhaust gas measuring method
CN106372806B (en) * 2016-09-12 2019-04-12 上海中船三井造船柴油机有限公司 For marine diesel engine CO2The measurement method and device of gas discharge
CN106372806A (en) * 2016-09-12 2017-02-01 上海中船三井造船柴油机有限公司 Measurement method and apparatus used for CO2 gas discharge of ship diesel engine
CN108414033A (en) * 2017-01-19 2018-08-17 株式会社堀场制作所 Extraction flow determination unit and exhaust gas analyzer
CN108414033B (en) * 2017-01-19 2021-01-01 株式会社堀场制作所 Exhaust gas flow rate measuring unit and exhaust gas analyzer
CN106932207A (en) * 2017-03-17 2017-07-07 广州汽车集团股份有限公司 Vehicle discharge scaling method and the system of vehicle
CN106932207B (en) * 2017-03-17 2019-02-05 广州汽车集团股份有限公司 The vehicle discharge scaling method and system of vehicle
CN106918637B (en) * 2017-04-14 2020-02-07 中国石油化工股份有限公司 On-line total hydrocarbon concentration monitoring device and method for gas treatment device
CN106918637A (en) * 2017-04-14 2017-07-04 中国石油化工股份有限公司 The online total hydrocarbon concentration monitoring device and method of gas treatment equipment
CN109425492A (en) * 2017-08-22 2019-03-05 上海汽车集团股份有限公司 A kind of fixed device and its installation method
CN109425492B (en) * 2017-08-22 2021-03-19 上海汽车集团股份有限公司 Fixing device and mounting method thereof
CN108918204A (en) * 2018-05-16 2018-11-30 南通大学 The portable gasoline vehicle particle sampling device of commercial PM sampling instrument can be connected
CN108692995A (en) * 2018-05-16 2018-10-23 南通大学 The Portable diesel vehicle particle sampling device of commercial PM sampling instruments can be connected
CN110987473A (en) * 2019-12-06 2020-04-10 辽宁龙马安泰网络技术有限责任公司 Distance correction method for transient fuel or waste gas of automobile bench test
CN110987473B (en) * 2019-12-06 2021-04-20 辽宁龙马安泰网络技术有限责任公司 Distance correction method for transient fuel or waste gas of automobile bench test
CN112730308A (en) * 2021-01-04 2021-04-30 东风汽车股份有限公司 Device and method for testing tail gas components of whole vehicle
CN117407827A (en) * 2023-12-15 2024-01-16 湖南辉达净化工程有限公司 Abnormal operation data detection method for purification engineering waste gas purification equipment
CN117407827B (en) * 2023-12-15 2024-02-13 湖南辉达净化工程有限公司 Abnormal operation data detection method for purification engineering waste gas purification equipment

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