Agricultural equipment emission index determination is the systematic measurement of regulated exhaust pollutants—such as CO, HC, NOx, PM and particle number—emitted by the diesel and gasoline engines installed in tractors, harvesters and other non-road agricultural machinery. Testing is carried out by accredited third-party laboratories in accordance with ISO 8178, GB 20891, EU Stage V (Regulation (EU) 2016/1628) and US EPA Tier 4 requirements, giving manufacturers the data required for type approval, production conformity and in-use compliance. This article explains the sample scope, testing items, analytical methods and typical applications of agricultural machinery emission measurement.
Technical Overview
Agricultural equipment emission index determination refers to the laboratory and field measurement of exhaust emissions produced by internal combustion engines and complete machines used in agricultural production. Because agricultural tractors, combine harvesters, rotary tillers and other non-road mobile machinery operate with diesel or gasoline engines over widely varying load profiles, regulators worldwide have established dedicated emission frameworks that differ from on-road vehicle standards. The measurement process quantifies brake-specific emissions, expressed in grams per kilowatt-hour (g/kWh), and compares the results against the applicable limit values.
The principal regulatory and technical references for this field include:
- ISO 8178 series (and its Chinese adoption GB/T 8190): exhaust emission measurement for reciprocating internal combustion engines, including test cycles, fuel specifications and analytical instrumentation.
- GB 20891: emission limits and measurement methods for diesel engines of non-road mobile machinery in China, covering Stage III and the current Stage IV (China IV) requirements.
- Regulation (EU) 2016/1628: the European Stage V framework for non-road mobile machinery, which introduced particle number (PN) limits for engines below 56 kW and 130 kW thresholds.
- US EPA 40 CFR Part 1039 for non-road diesel engines (Tier 4) and 40 CFR Parts 90/1054 for small spark-ignition engines.
- GB 3847 and the European Load Response (ELR) procedure for smoke opacity measurement of compression-ignition engines.
- ISO 14396 for net power determination, which is essential for calculating brake-specific emission factors.
Accredited third-party laboratories perform these determinations using engine dynamometers, dilution tunnels, gas analyzers and portable emissions measurement systems (PEMS), and the resulting reports support certification, subsidy listing, quality control and product development.
Testing Samples
Non-Road Diesel Engines for Agricultural Machinery
Standalone diesel engines intended for installation in tractors, harvesters and other agricultural machines form the core sample category. Type-approval testing is usually conducted at engine level, with the engine mounted on a dynamometer test bench and equipped with its production intake, exhaust and after-treatment systems, including diesel oxidation catalysts (DOC), diesel particulate filters (DPF) and selective catalytic reduction (SCR) units where applicable.
Tractors and Self-Propelled Agricultural Machinery
Complete machines, such as wheeled or crawler tractors, combine harvesters, self-propelled sprayers, forage harvesters and cotton pickers, may be tested for machine-level verification, in-service conformity or smoke opacity checks. Field measurements on complete machines are typically performed with PEMS instrumentation installed on the operating vehicle under real agricultural working conditions.
Small Gasoline Engines and Hand-Held Equipment
Spark-ignition engines below 19 kW used in hand-held or hand-carried agricultural equipment—such as backpack sprayers, brush cutters, chain saws and small tillers—are tested against small-SI engine standards. These engines are frequently evaluated using the ISO 8178 D2 or dedicated small-engine cycles, with hydrocarbon and NOx limits expressed in g/kWh.
Other Agricultural Power Units
Diesel generator sets for irrigation and farm power supply, power sprayers, rice transplanters, micro-tilling machines and agricultural transport vehicles are also submitted for emission determination, either for regulatory compliance, market access or machinery purchase subsidy programs.
Testing Items
The key emission indices determined for agricultural equipment include:
- Carbon monoxide (CO), reported in g/kWh as a brake-specific mass emission.
- Total hydrocarbons (THC) and, for some engine categories, non-methane hydrocarbons (NMHC).
- Oxides of nitrogen (NOx), including direct NO2 measurement for after-treatment-equipped engines.
- Particulate matter (PM) mass emissions collected on filter media and determined gravimetrically.
- Particle number (PN) concentration, required for Stage V engines in the relevant power bands.
- Smoke opacity, expressed as the light absorption coefficient (m⁻¹), measured under free acceleration or load-response conditions.
- Carbon dioxide (CO2) and fuel consumption, often recorded simultaneously for energy-efficiency evaluation.
- Crankcase emissions, which must be demonstrated as closed or fully burned for many engine categories.
- Deterioration factors and durability demonstration over the assigned useful life period.
- In-use emissions, principally NOx, CO and PN, measured with PEMS during representative agricultural duty.
Depending on the purpose of the determination, additional indices such as ammonia (NH3) slip from SCR systems may also be quantified.
Testing Methods
Steady-State Cycle Testing (NRSC)
The non-road steady-state cycle is based on the ISO 8178 test modes. The universal 8-mode C1 cycle is applied to most variable-speed agricultural diesel engines, while constant-speed engines use the D1 or D2 cycles and hand-held equipment may use the G1, G2 or G3 cycles. The engine is stabilized at each mode, exhaust is sampled, and weighted results are combined into brake-specific values referenced to the measured power per ISO 14396.
Transient Cycle Testing (NRTC)
Stage IIIa and later non-road diesel engines are additionally evaluated over the non-road transient cycle, a 1238-second engine-speed-and-torque profile designed to reproduce real agricultural duty. Stage IV and Stage V testing requires the NRTC to be run both with a cold start after engine soaking and with a hot start, with weighting factors applied to the two results.
Gaseous and Particulate Measurement Techniques
Raw or diluted exhaust is analyzed using reference instrumentation: non-dispersive infrared (NDIR) analyzers for CO and CO2, heated flame ionization detectors (HFID) for hydrocarbons, and chemiluminescent detectors (CLD) for NOx. Particulate matter is determined gravimetrically from filters loaded in a full-flow dilution tunnel, or with partial-flow dilution systems meeting ISO 8178-1 criteria. Particle number is measured with a condensation particle counter downstream of a volatile particle remover, following the protocol defined in the Stage V regulation.
Smoke Opacity Testing
Compression-ignition engines are subjected to the European Load Response (ELR) test or, for in-service machines, the free-acceleration smoke test per GB 3847. An opacimeter measures the light absorption coefficient across the exhaust stream at defined load steps or during free acceleration, and the peak values are compared with the applicable limits.
Portable Emissions Measurement (PEMS)
For in-service monitoring and field verification, portable analyzers are installed on operating agricultural machinery. NOx, CO, PN and exhaust mass flow are recorded in real time during plowing, harvesting or transport operations, and the data are post-processed with the normalization methods specified by the relevant in-service conformity provisions to verify that after-treatment systems perform as designed throughout the useful life.
Applications
Emission index determination for agricultural equipment serves multiple industry purposes:
- Type approval and certification of engines and machinery for the Chinese market under GB 20891, including the Stage IV requirements with mandatory NRTC and after-treatment verification.
- Export compliance testing against EU Stage V and US EPA Tier 4 limits for manufacturers shipping agricultural machinery internationally.
- Inclusion in government agricultural machinery purchase subsidy catalogs, which typically require valid emission compliance documentation.
- Production conformity evaluation, verifying that serial-production engines continue to match the certified reference emissions.
- Research, development and calibration of combustion systems, EGR strategies, DOC, DPF and SCR after-treatment components.
- In-use compliance programs and field audits of fleet machinery, including smoke opacity screening of older diesel equipment.
- Import inspection, market surveillance and dispute resolution between equipment suppliers and purchasers.
FAQ
What is the difference between the NRSC and NRTC test cycles?
The NRSC is a steady-state cycle composed of discrete engine operating modes with fixed weighting factors, while the NRTC is a second-by-second transient profile that reproduces real agricultural load changes. Modern Stage IIIa and later engines generally require both cycles, with Stage IV and Stage V adding cold-start weighting.
Why is particle number (PN) now measured in addition to PM mass?
Particle mass alone does not reflect the number of ultrafine particles emitted by engines equipped with advanced fuel injection and after-treatment systems. The PN limit, introduced under Stage V, uses condensation particle counting to control fine particle emissions more effectively than gravimetric PM alone.
How long does a typical emission determination take?
A complete engine-bench determination, including engine mapping, cycle validation, gaseous and particulate sampling, and reporting, usually requires one to several weeks depending on engine category, the number of test cycles, cold-soak requirements and whether durability or PEMS work is included.
Can complete agricultural machines be tested instead of engines?
Yes. Regulatory type approval is primarily engine-based, but complete machines can be evaluated for smoke opacity, in-service conformity and field performance using PEMS instrumentation installed on the operating vehicle.
What information should be provided when submitting a sample?
The laboratory typically needs the engine or machine technical specifications, rated and intermediate speed data, the declared power curve, after-treatment configuration, intended certification stage or market, applicable parent-engine family information, and the relevant standards to which the results must be reported.
How are emissions expressed and compared with limits?
All gaseous and particulate results are converted into brake-specific mass emissions in g/kWh by relating measured pollutant mass to the work produced over the cycle, after applying humidity and NOx corrections where required. The weighted cycle values are then compared directly with the limit values of the applicable emission stage.