[Code of Federal Regulations]

[Title 40, Volume 31]

[Revised as of July 1, 2006]

From the U.S. Government Printing Office via GPO Access

[CITE: 40CFR1065.140]



[Page 689-691]

 

                   TITLE 40--PROTECTION OF ENVIRONMENT

 

         CHAPTER I--ENVIRONMENTAL PROTECTION AGENCY (CONTINUED)

 

PART 1065_ENGINE-TESTING PROCEDURES--Table of Contents

 

                   Subpart B_Equipment Specifications

 

Sec.  1065.140  Dilution for gaseous and PM constituents.



    (a) General. You may dilute exhaust with ambient air, synthetic air, 

or nitrogen that is at least 15 [deg]C. Note that the composition of the 

diluent affects some gaseous emission measurement instruments' response 

to emissions. We recommend diluting exhaust at a location as close as 

possible to the location where ambient air dilution would occur in use.

    (b) Dilution-air conditions and background concentrations. Before a 

diluent is mixed with exhaust, you may precondition it by increasing or 

decreasing its temperature or humidity. You may also remove constituents 

to reduce their background concentrations. The following provisions 

apply to removing constituents or accounting for background 

concentrations:

    (1) You may measure constituent concentrations in the diluent and 

compensate for background effects on test results. See Sec.  1065.650 

for calculations that compensate for background concentrations.

    (2) Either measure these background concentrations the same way you 

measure diluted exhaust constituents, or measure them in a way that does 

not affect your ability to demonstrate compliance with the applicable 

standards. For example, you may use the following simplifications for 

background sampling:

    (i) You may disregard any proportional sampling requirements.

    (ii) You may use unheated gaseous sampling systems.

    (iii) You may use unheated PM sampling systems only if we approve it 

in advance.

    (iv) You may use continuous sampling if you use batch sampling for 

diluted emissions.

    (v) You may use batch sampling if you use continuous sampling for 

diluted emissions.

    (3) For removing background PM, we recommend that you filter all 

dilution air, including primary full-flow dilution air, with high-

efficiency particulate air (HEPA) filters that have an initial minimum 

collection efficiency specification of 99.97% (see Sec.  1065.1001 for 

procedures related to HEPA-filtration efficiencies). Ensure that HEPA 

filters are installed properly so that background PM does not leak past 

the HEPA filters. If you choose to correct for background PM without 

using HEPA filtration, demonstrate that the background PM in the 

dilution air contributes less than 50% to the net PM collected on the 

sample filter.

    (c) Full-flow dilution; constant-volume sampling (CVS). You may 

dilute the full flow of raw exhaust in a dilution tunnel that maintains 

a nominally constant volume flow rate, molar flow rate or mass flow rate 

of diluted exhaust, as follows:

    (1) Construction. Use a tunnel with inside surfaces of 300 series 

stainless steel. Electrically ground the entire dilution tunnel. We 

recommend a thin-walled and insulated dilution tunnel to minimize 

temperature differences between the wall and the exhaust gases.

    (2) Pressure control. Maintain static pressure at the location where 

raw exhaust is introduced into the tunnel within 1.2 kPa of atmospheric 

pressure. You may use a booster blower to control this pressure. If you 

test an engine using more careful pressure control and you show by 

engineering analysis or by test data that you require this level of 

control to demonstrate compliance at the applicable standards, we will 

maintain the same level of static pressure control when we test that 

engine.

    (3) Mixing. Introduce raw exhaust into the tunnel by directing it 

downstream along the centerline of the tunnel. You may introduce a 

fraction of dilution air radially from the tunnel's inner surface to 

minimize exhaust interaction with the tunnel walls. You may configure 

the system with turbulence generators such as orifice plates or fins to 

achieve good mixing. We recommend a minimum Reynolds number,



[[Page 690]]



Re#, of 4000 for the diluted exhaust stream, where Re# is based on the 

inside diameter of the dilution tunnel. Re# is defined in Sec.  

1065.640.

    (4) Flow measurement preconditioning. You may condition the diluted 

exhaust before measuring its flow rate, as long as this conditioning 

takes place downstream of any sample probes, as follows:

    (i) You may use flow straighteners, pulsation dampeners, or both of 

these.

    (ii) You may use a filter.

    (iii) You may use a heat exchanger to control the temperature 

upstream of any flow meter. Note paragraph (c)(6) of this section 

regarding aqueous condensation.

    (5) Flow measurement. Section 1065.240 describes measurement 

instruments for diluted exhaust flow.

    (6) Aqueous condensation. You may either prevent aqueous 

condensation throughout the dilution tunnel or you may measure humidity 

at the flow meter inlet. Calculations in Sec.  1065.645 and Sec.  

1065.650 account for either method of addressing humidity in the diluted 

exhaust. Note that preventing aqueous condensation involves more than 

keeping pure water in a vapor phase (see Sec.  1065.1001).

    (7) Flow compensation. Maintain nominally constant molar, volumetric 

or mass flow of diluted exhaust. You may maintain nominally constant 

flow by either maintaining the temperature and pressure at the flow 

meter or by directly controlling the flow of diluted exhaust. You may 

also directly control the flow of proportional samplers to maintain 

proportional sampling. For an individual test, validate proportional 

sampling as described in Sec.  1065.545.

    (d) Partial-flow dilution (PFD). Except as specified in this 

paragraph (d), you may dilute a partial flow of raw or previously 

diluted exhaust before measuring emissions. Sec.  1065.240 describes 

PFD-related flow measurement instruments. PFD may consist of constant or 

varying dilution ratios as described in paragraphs (d)(2) and (3) of 

this section. An example of a constant dilution ratio PFD is a 

``secondary dilution PM'' measurement system. An example of a varying 

dilution ratio PFD is a ``bag mini-diluter'' or BMD.

    (1) Applicability. (i) You may not use PFD if the standard-setting 

part prohibits it.

    (ii) You may use PFD to extract a proportional raw exhaust sample 

for any batch or continuous PM emission sampling over any transient duty 

cycle only if we have explicitly approved it according to Sec.  1065.10 

as an alternative procedure to the specified procedure for full-flow 

CVS.

    (iii) You may use PFD to extract a proportional raw exhaust sample 

for any batch or continuous gaseous emission sampling.

    (iv) You may use PFD to extract a proportional raw exhaust sample 

for any batch or continuous PM emission sampling over any steady-state 

duty cycle or its ramped-modal cycle (RMC) equivalent.

    (v) You may use PFD to extract a proportional raw exhaust sample for 

any batch or continuous field-testing.

    (vi) You may use PFD to extract a proportional diluted exhaust 

sample from a CVS for any batch or continuous emission sampling.

    (vii) You may use PFD to extract a constant raw or diluted exhaust 

sample for any continuous emission sampling.

    (2) Constant dilution-ratio PFD. Do one of the following for 

constant dilution-ratio PFD:

    (i) Dilute an already proportional flow. For example, you may do 

this as a way of performing secondary dilution from a CVS tunnel to 

achieve temperature control for PM sampling.

    (ii) Continuously measure constituent concentrations. For example, 

you might dilute to precondition a sample of raw exhaust to control its 

temperature, humidity, or constituent concentrations upstream of 

continuous analyzers. In this case, you must take into account the 

dilution ratio before multiplying the continuous concentration by the 

sampled exhaust flow rate.

    (iii) Extract a proportional sample from the constant dilution ratio 

PFD system. For example, you might use a variable-flow pump to 

proportionally fill a gaseous storage medium such as a bag from a PFD 

system. In this case, the proportional sampling must meet the same 

specifications as varying dilution ratio PFD in paragraph (d)(3) of this 

section.



[[Page 691]]



    (3) Varying dilution-ratio PFD. All the following provisions apply 

for varying dilution-ratio PFD:

    (i) Use a control system with sensors and actuators that can 

maintain proportional sampling over intervals as short as 200 ms (i.e., 

5 Hz control).

    (ii) For control input, you may use any sensor output from one or 

more measurements; for example, intake-air flow, fuel flow, exhaust 

flow, engine speed, and intake manifold temperature and pressure.

    (iii) Account for any emission transit time in the PFD system.

    (iv) You may use preprogrammed data if they have been determined for 

the specific test site, duty cycle, and test engine from which you 

dilute emissions.

    (v) We recommend that you run practice cycles to meet the validation 

criteria in Sec.  1065.545. Note that you must validate every emission 

test by meeting the validation criteria with the data from that specific 

test, not from practice cycles or other tests.

    (vi) You may not use a PFD system that requires preparatory tuning 

or calibration with a CVS or with the emission results from a CVS. 

Rather, you must be able to independently calibrate the PFD.

    (e) Dilution and temperature control of PM samples. Dilute PM 

samples at least once upstream of transfer lines. You may dilute PM 

samples upstream of a transfer line using full-flow dilution, or 

partial-flow dilution immediately downstream of a PM probe. Control 

sample temperature to a (47 5) [deg]C tolerance, 

as measured anywhere within 20 cm upstream or downstream of the PM 

storage media (such as a filter). Measure this temperature with a bare-

wire junction thermocouple with wires that are (0.500 0.025) mm diameter, or with another suitable instrument 

that has equivalent performance. Heat or cool the PM sample primarily by 

dilution.