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Prepared by 

S. McGinn 

Noranda Inc. - Technology Centre, Pointe Claire, Québec 

With contributions from 

M. Grenier, M. Gangal, and B. Rubeli 

Natural Resources Canada, CANMET, Sudbury and Bells Corners, Ontario, Canada 

A. Bugarksi and G. Schnakenberg 

NIOSH - Pittsburgh Research Laboratory, Pittsburgh, Pennsylvania, U.S.A. 

R. Johnson, D. Petrie, and G. Crowther 

Noranda Inc. – Brunswick Mine, Bathurst, New Brunswick, Canada 

J. Penney 

United Steelworkers of America, Toronto, Ontario, Canada 
 - 2 -

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This report is a summary of the investigation and findings of nearly three years of field 

and laboratory work looking at diesel particulate filter (DPF) systems. An investigation 

of this length and scope requires strong collaboration from many organizations and 

individuals. Though the list of individuals is too long to acknowledge here it is important 

to make note of their organizations. 

By far the most important collaboration in this project came from the people at Noranda 

Inc. – Brunswick Mine. The management, engineering, production and maintenance 

people formed a large project team on their own to ensure that the project was supported 

by all mine groups from beginning to end. The commitment of Brunswick Mine to this 

project was the single most critical factor in its success. 

In terms of research collaboration many organizations were active participants. Natural 

Resources Canada – CANMET played a large role with laboratories from both Sudbury, 

Ontario and Bells Corners, Ontario participating in field work, laboratory work, and 

reporting. The Pittsburgh Research Laboratory - NIOSH group participated in field 

research from beginning to end of the project and contributed to reporting. The VERT 

program in Switzerland contributed background information and advice in building the 

scope of the project. The United Steelworkers of America participated in building the 

scope of the project, following the progress and making recommendations during the 

course of the project and contributed to reporting and editing. The technical committee of 

the Diesel Emissions Evaluation Program (DEEP) followed the project from conception 

to final report providing critical input and feedback to ensure a successful project. 

The vehicle, engine, and emissions controls manufacturers each contributed technical 

expertise, information and specifications, and materials needed to keep the project 

running successfully. Atlas Copco Construction and Mining Equipment assisted in 

providing materials for the four vehicles in the project. Detroit Diesel Corporation 

collaborated for support of the four engines in the project. The four DPF systems came 

from Engine Control Systems – Lubrizol Canada Ltd. of Toronto, Ontario, DCL 

International of Toronto, Ontario, Oberland Mangold of Germany, and Catalytic Exhaust 

Products of Toronto Ontario. Octel Corporation of Bletchley, United Kingdom provided 

the fuel additive used in the project and technical support during the project. Each of the 

DPF manufacturers actively participated collaboratively in design, installation and 

support of the DPF systems from beginning to end of the project. 

The project sponsor, the Diesel Emissions Evaluation Program (DEEP) would like to take 

this opportunity to thank all participants for their efforts in making this project a success. 

Sean McGinn 

Project Leader 
 - 3 -

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EXECUTIVE SUMMARY ................................................................................................. - 8 - 

ABOUT THE PROJECT .................................................................................................... - 8 - 

BACKGROUND AND OBJECTIVE .................................................................................... - 8 - 

PROJECT METHODOLOGY ............................................................................................. - 8 - 

Emissions Measurement .....................................................................................................................- 9 -

Ambient DPM Sampling.....................................................................................................................- 9 -

Vehicle and DPF Operating Statistics................................................................................................- 9 -

DPF SYSTEMS EXPERIENCE.......................................................................................... - 9 - 

ECS Catalyzed Filter..........................................................................................................................- 9 -

ECS Octel Filter...............................................................................................................................- 10 -

DCL Catalyzed/Electric Filter..........................................................................................................- 10 -

Oberland Mangold Octel Filter........................................................................................................- 10 -

CONCLUSIONS ............................................................................................................ - 11 - 

INTRODUCTION TO RESEARCH.................................................................................... - 12 - 

Background ......................................................................................................................................- 12 -

Project Objectives ............................................................................................................................- 12 -

Project Scope and Structure .............................................................................................................- 13 -

DPF Selection Process and Methodology ........................................................................................- 14 -

DPF Evaluation Methodology..........................................................................................................- 19 -

DIESEL PARTICULATE FILTER SYSTEMS APPLICATIONS AND SPECIFICATIONS ........... - 27 - 

Proposals and Selection ...................................................................................................................- 27 -

DPF Installations .............................................................................................................................- 30 -

Baseline Performance Measurements ..............................................................................................- 41 -

FIELD PERFORMANCE EVALUATIONS ......................................................................... - 43 - 

Methods............................................................................................................................................- 43 -

Results ..............................................................................................................................................- 44 -

ECS CatTrap DPF System Installed on LHD VL244 ....................................................................................- 44 - 4

Chronology of Events....................................................................................................................................- 45 -

Exhaust Temperature and Backpressure ........................................................................................................- 45 -

Gaseous Emissions ........................................................................................................................................- 46 -

Diesel Particulate Matter (DPM) Emissions ..................................................................................................- 47 -

Observations ..................................................................................................................................................- 49 -

DCL Bluesky System Installed On LHD VL247................................................................................- 50 -

Chronology of Events....................................................................................................................................- 50 -

Exhaust Temperature and Backpressure ........................................................................................................- 51 -

Gaseous Emissions ........................................................................................................................................- 52 -

Diesel Particulate Matter (DPM) Emissions ..................................................................................................- 53 -

Observations ..................................................................................................................................................- 54 -

ECS Octel System Installed on VH183 Truck...................................................................................- 55 -

Chronology of Events....................................................................................................................................- 56 -

Exhaust Temperature and Backpressure ........................................................................................................- 56 -

Gaseous Emissions ........................................................................................................................................- 57 -

Diesel Particulate Matter (DPM) Emissions ..................................................................................................- 59 -

Observations ..................................................................................................................................................- 60 -

Oberland Mangold Octel DPF System Installed on VH181 Truck...................................................- 61 -

Chronology of Events....................................................................................................................................- 61 -

Exhaust Temperature and Backpressure ........................................................................................................- 62 -

Gaseous Emissions ........................................................................................................................................- 63 -

Diesel Particulate Matter (DPM) Emissions ..................................................................................................- 64 -

Observations ..................................................................................................................................................- 65 -

ISOLATED ZONE STUDY.............................................................................................. - 66 - 
 - 4 -

Objective and Scope .........................................................................................................................- 66 -

Experiment Methodology..................................................................................................................- 66 -

Measurement of Ambient Concentrations of DPM...........................................................................- 68 -

LABORATORY EVALUATION OF DPF SYSTEMS........................................................... - 74 - 

Laboratory Bench Testing ................................................................................................................- 74 -

Post Study Inspections......................................................................................................................- 79 -

ECS CatTrap..................................................................................................................................................- 79 -

DCL Bluesky .................................................................................................................................................- 80 -

ECS Octel ......................................................................................................................................................- 81 -

Oberland Mangold Octel ...............................................................................................................................- 82 -

CONCLUSION .............................................................................................................. - 83 - 

RECOMMENDATIONS .................................................................................................. - 87 - Selection ........................................................................................................................................................- 87 -

Installation .....................................................................................................................................................- 87 -

Measurement .................................................................................................................................................- 88 -

Maintenance ..................................................................................................................................................- 88 -

Verification....................................................................................................................................................- 88 -

REFERENCES............................................................................................................... - 89 - 
 - 5 -

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FIGURE 1 - ATLAS COPCO WAGNER ST8B SCOOPTRAM®®®......................................................................... - 16 -

FIGURE 2 – ATLAS COPCO WAGNER MT436-B HAULAGE TRUCK............................................................ - 17 -

FIGURE 3 - ST8-B SCOOPTRAM® DUTY CYCLE ........................................................................................ - 18 -

FIGURE 4 - MT436-B TRUCK DUTY CYCLE .............................................................................................. - 19 -

FIGURE 5 - UGAS EMISSIONS TESTING SYSTEM ....................................................................................... - 21 -

FIGURE 6 - NANOMET DIESEL PARTICULATE ANALYSIS SYSTEM ............................................................. - 22 -

FIGURE 7 - RCD AND NIOSH 5040 OPERATOR DPM SAMPLING TRAINS ................................................. - 24 -

FIGURE 8 - METHOD 5040 ANALYSIS EXAMPLE........................................................................................ - 25 -

FIGURE 9 - DDEC REPORTS ENGINE OPERATING STATISTICS................................................................... - 26 -

FIGURE 10 - ECS CATTRAP CERAMIC MONOLITHS................................................................................... - 28 -

FIGURE 11 - ECS OCTEL DPF COMPONENTS ............................................................................................ - 28 -

FIGURE 12 - DCL BLUESKY DPF SILICON CARBIDE MONOLITH AND HEATER ELEMENT ......................... - 29 -

FIGURE 13 - OBERLAND MANGOLD DPF GLASS FIBER CARTRIDGES........................................................ - 30 -

FIGURE 14 - ECS CATTRAP INSTALLATION............................................................................................... - 31 -

FIGURE 15 - DCL BLUESKY INSTALLATION ON VL247............................................................................. - 33 -

FIGURE 16 - DCL REGENERATION PLUG IN UNIT...................................................................................... - 34 -

FIGURE 17 - ECS OCTEL INSTALLATION ON VH183 ................................................................................. - 35 -

FIGURE 18 - EXHAUST TEMPERATURE AND BACKPRESSURE TRACES FOR FIRST OBERLAND MANGOLD DPF . -

37 -

FIGURE 19 - ORIGINAL OBERLAND MANGOLD DPF INSTALLATION.......................................................... - 38 -

FIGURE 20 - FINAL OBERLAND MANGOLD DPF INSTALLATION................................................................ - 38 -

FIGURE 21 - BLENDED FUEL STORAGE ON SURFACE................................................................................. - 40 -

FIGURE 22 - BLENDED FUEL STORAGE AT 1000 LEVEL............................................................................. - 40 -

FIGURE 23 - ECS CATTRAP EXHAUST TEMPERATURE AND BACKPRESSURE............................................. - 46 -

FIGURE 24 – GASEOUS EMISSIONS FOR VL244 WITH ECS CATTRAP....................................................... - 47 -

FIGURE 25 – DPM FILTRATION EFFICIENCIES FOR ECS CATTRAP DPF SYSTEM ..................................... - 48 -

FIGURE 26 – BACHARACH SMOKE INDEX MEASURED FOR ECS CATTRAP DPF SYSTEM.......................... - 49 -

FIGURE 27 - EXHAUST TEMPERATURES AND ENGINE BACKPRESSURES RECORDED FOR LHD VH247 EQUIPPED 

WITH DCL BLUESKY DPF SYSTEM ................................................................................................... - 51 -

FIGURE 28 - GASEOUS EMISSIONS FOR VL247 WITH DCL BLUESKY DPF SYSTEM ................................. - 52 -

FIGURE 29 - DPM FILTRATION EFFICIENCIES FOR DCL BLUESKY DPF SYSTEM...................................... - 53 -

FIGURE 30 – BACHARACH SMOKE DENSITY RESULTS ON VL247 WITH DCL BLUSEKY DPF SYSTEM...... - 54 -

FIGURE 31 - ECS OCTEL EXHAUST TEMPERATURE AND BACKPRESSURE ................................................. - 57 -

FIGURE 32 - GASEOUS EMISSIONS FOR VH183 ECS OCTEL DPF SYSTEM................................................ - 58 -

FIGURE 33 – DPM FILTRATION EFFICIENCIES FOR ECS OCTEL DPF SYSTEM ON VH183 TRUCK............. - 59 -

FIGURE 34 - BACHARACH SMOKE DENSITY RESULTS ON VH183 WITH ECS OCTEL DPF SYSTEM........... - 60 -

FIGURE 35 - OBERLAND MANGOLD EXHAUST TEMPERATURE AND BACKPRESSURE................................. - 62 -

FIGURE 36 – GASEOUS EMISSIONS FOR VH181 WITH OBERLAND MANGOLD DPF .................................. - 63 -

FIGURE 37 – DPM FILTRATION EFFICIENCIES FOR OBERLAND MANGOLD DPF SYSTEM ON VH181 TRUCK .. -

64 -

FIGURE 38 - OBERLAND MANGOLD OCTEL BACHARACH SMOKE DENSITY RESULTS ............................... - 65 -

FIGURE 39 - 525-5 SUBLEVEL ISOLATED ZONE ......................................................................................... - 67 -

FIGURE 40 – TOTAL CARBON CONCENTRATIONS IN ISOLATED ZONE FOR DIFFERENT TEST VEHICLES..... - 69 -

FIGURE 41 - ELEMENTAL CARBON CONCENTRATIONS IN ISOLATED ZONE FOR DIFFERENT TEST VEHICLES- 70

-

FIGURE 42 - PARTICLE CONCENTRATIONS BY NUMBER MEASURED IN ISOLATED ZONE FOR DIFFERENT TEST 

VEHICLES .......................................................................................................................................... - 71 -

FIGURE 43 - PARTICLE CONCENTRATIONS BY VOLUME MEASURED IN ISOLATED ZONE FOR DIFFERENT TEST 

VEHICLES .......................................................................................................................................... - 72 -

FIGURE 44 – RESULTS OF MEASUREMENT WITH PAS 2000, MINE TEST CYCLES ...................................... - 75 -

FIGURE 45 – RESULTS OF MEASUREMENT WITH PAS 2000, SNAP ACCELERATION NO-LOAD TESTS........ - 76 -

FIGURE 46 – RESULTS OF MEASUREMENT WITH PAS 2000, SNAP ACCELERATION UNDER LOAD TESTS .. - 76 -

FIGURE 47 – AVERAGE TOTAL DPM EMISSIONS OVER FOUR-MODE TESTS ............................................. - 77 -

FIGURE 48 – AVERAGE CARBON MONOXIDE EMISSIONS MEASURED OVER FOUR-MODE TESTS.............. - 78 -
 - 6 -

FIGURE 49 – AVERAGE HYDROCARBON EMISSIONS MEASURED OVER FOUR-MODE TESTS ..................... - 78 -

FIGURE 50 – AVERAGE NITROGEN DIOXIDE EMISSIONS MEASURED ACROSS FOUR-MODE TESTS ........... - 79 -

FIGURE 51 - NON-DESTRUCTIVE TESTING OF ECS CATTRAP ................................................................... - 80 -

FIGURE 52 - INLET AND OUTLET FACES OF DCL BLUESKY DPF............................................................... - 81 -

FIGURE 53 - INLET AND OUTLET FACES OF ECS OCTEL DPF.................................................................... - 82 -

FIGURE 54 - OBERLAND MANGOLD FIBER CARTRIDGES AND IRON OXIDE ACCUMULATION .................... - 83 -
 - 7 -

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TABLE 1 - ATLAS COPCO WAGNER ST8B SCOOPTRAM®®®SPECIFICATIONS ................................................ - 16 -

TABLE 2 - ATLAS COPCO WAGNER MT436B HAULAGE TRUCK SPECIFICATIONS..................................... - 17 -

TABLE 3 - ECOM AC GAS ANALYZER PARAMETERS ............................................................................... - 20 -

TABLE 4 - ECS CATTRAP INSTALLATION ON VL244 SCOOPTRAM............................................................ - 31 -

TABLE 5 - DCL BLUESKY INSTALLATION ON VL247 SCOOPTRAM ........................................................... - 33 -

TABLE 6 - ECS OCTEL INSTALLATION ON VH183 TRUCK ........................................................................ - 35 -

TABLE 7 - OBERLAND MANGOLD DPF SYSTEM INSTALLATED ON VH181 HAULAGE TRUCK................... - 37 -

TABLE 8 - BASELINE EMISSIONS AND EXHAUST PROPERTIES ESTABLISH FOLLOWING INSTALLATION OF ECS

CATTRAP DPF SYSTEM ON LHD VL244........................................................................................... - 41 -

TABLE 9 - BASELINE EMISSIONS AND EXHAUST PROPERTIES ESTABLISH FOLLOWING INSTALLATION OF DCL

BLUESKY DPF SYSTEM ON LHD VL247........................................................................................... - 41 -

TABLE 10 - BASELINE EMISSIONS AND EXHAUST PROPERTIES ESTABLISHED FOLLOWING INSTALLATION OF 

ECS OCTEL DPF SYSTEM ON VH183 TRUCK .................................................................................... - 42 -

TABLE 11 - BASELINE EMISSIONS AND EXHAUST PROPERTIES ESTABLISH FOLLOWING INSTALLATION OF 

OBERLAND MANGOLD DPF SYSTEM ON VH181 TRUCK.................................................................... - 42 -

TABLE 12 - LABORATORY BENCH TEST PARAMETERS AND PROTOCOL .................................................... - 74 -
 - 8 -

EEXXEEECCCUUUTTTIIIVVVEEE SSUUUMMMMMMAAARRRYYY

About the Project 

The Brunswick Mine Diesel Particulate Filter Study was one of several research projects 

initiated by the Diesel Emissions Evaluation Program (DEEP). The study was carried out 

at Noranda’s Brunswick Mine in Bathurst, New Brunswick by Noranda Technology 

Centre and Brunswick Mine personnel with the collaboration of Natural Resources 

Canada - Canada Centre for Minerals and Energy Technology (CANMET), National 

Institute of Occupational Safety and Health (NIOSH), Andreas Mayer of VERT, and 

diesel particulate filter (DPF) system suppliers. 

The study began in early 2000. Field evaluations continued for 20 months. The final 

report—authored by Sean McGinn—was submitted to DEEP in the Autumn of 2003. 

Background and Objective 

The DEEP program had identified diesel particulate filter (DPF) systems as the most 

promising technology to provide 90% or better reduction in particulate matter emissions 

from diesel-powered underground mining vehicles [Mayer A. 1998]. The purpose of the 

Noranda Brunswick Mine project was to determine the effectiveness, durability, 

reliability, and economic viability of current generation DPF technology when applied in 

underground mining operations. 

The Noranda project team selected four heavy-duty production vehicles to be tested with 

DPF systems over a period of 4000 hours. Two of the vehicles were load-haul-dump 

(LHD) vehicles (Atlas Copco, Portland, Oregon, Model ST8-B Scooptram®). These 

vehicles are used as front-end loaders to dig into a pile of ore, tram the load over a 

distance, dump it to a transfer point, and return to the load point to repeat the cycle. The 

other two vehicles were haulage trucks (Atlas Copco, Portland, Oregon, Model MT436-

B). These trucks are designed to haul large loads over long distances. The trucks are 

typically loaded either by an LHD or at an overhead chute. All four vehicles were 

powered by electronically controlled turbocharged and intercooled engines (Detroit 

Diesel Corporation, Series 60). The engines in LHDs were rated at 242 kW (325 hp). The 

engines in trucks were rated at 278 kW (375 hp). 

At the initial stage of the project the request for proposals (RFP) was submitted to 

particulate filter manufacturers. The RFP contained detailed description of the vehicles 

and their duty cycles, including recordings of exhaust gas temperatures. Based on 

provided information, the emission control manufacturers produced proposals for 

particulate filter systems for each of the applications. 

Project Methodology 

Performance of the DPF systems during the project was evaluated using: 
 - 9 -

 Quantitative assessments, including (1) measurements of the effects of the systems 

on tailpipe emissions, (2) measurements of the effects of the systems on ambient 

concentrations of diesel particulate matter and selected gases, and (3) gathering 

vehicle and DPF operating parameters and statistics, and 

 Qualitative feedback information, logged from vehicle operators, mechanics, 

maintenance crew, and mine management. 

Emissions Measurement 

Instruments and methods were developed to accommodate the day to day monitoring, as 

well as more detailed periodic scientific evaluations performed at regular intervals. 

Tailpipe emissions were measured using an ECOM AC emissions analyzer (Ecom 

America, Norcross, Georgia) and the NanoMet diesel particulate characterization system 

(Matter Engineering, Switzerland) —an instrument incorporating a diffusion charger 

(DC) and a photoelectric aerosol sensors (PAS). 

Ambient DPM Sampling 

Sampling and analysis was conducted through the project for ambient concentrations of 

diesel particulate matter. The samples collected during this study were analyzed for 

carbon content using the Respirable Combustible Dust (RCD) method and the NIOSH 

Analytical Method 5040. 

Vehicle and DPF Operating Statistics 

The data on operating hours, fuel consumption, idling hours, and operating profiles with 

engine speed and load versus time were obtained from engine electronic control modules 

(ECM) using software supplied by the engine manufacturer. The performance of DPF 

systems was monitored by datalogging exhaust temperatures and backpressures. This was 

particularly important for assessment of the regeneration process of DPF systems. 

DPF Systems Experience 

ECS Catalyzed Filter 

The ECS filter comprised a cordierite wall-flow monolith coated with a base metal 

catalyst. The system was designed to promote passive regeneration – that is, to 

automatically burn off accumulated soot without operator intervention. This filter 

performed well in all aspects (emissions, regeneration, robustness, maintenance 

requirement) during the study. It accumulated a total of 4053 operating hours. The system 

measured between 99 and 100% filtration efficiency of elemental carbon particles when 

installed new and continued to perform at better than 96% efficiency with 4000 operating 

hours on it. 
- 10 - 

ECS Octel Filter 

The ECS Octel filter utilized two parallel silicon carbide (SiC) substrates with oxidation 

catalysts in the upstream position. The filter was passively regenerated using Octimax 

4804 iron/strontium (Fe/Sr) based fuel additive by Octel [Vincent et al. 2000]. The 

additive was expected to lower the temperature at which the regeneration process is 

initiated. The additive was blended to the fuel in a separate fueling system maintained for 

the two vehicles with additive-assisted DPFs. The concentration of metals in the fuel was 

20 ppm, with a 16:4 Fe:Sr ratio. 

After an initial period of satisfactory operation, this filter started building excessive 

engine backpressure. This was due to slow regeneration that occurred despite high 

exhaust temperatures. After some time the filter substrate failure occurred due to 

uncontrolled regeneration of the overloaded filter. A replacement unit was also damaged 

due to uncontrolled regeneration. The first filter unit accumulated over 2500 operating 

hours. The second unit was removed from the vehicle after approximately 1620 hours. 

DCL Catalyzed/Electric Filter 

The DCL DPF system utilized platinum-catalyzed SiC substrate. The active DPF system 

was also equipped with a 600 V electric heater installed at the inlet face of the filter 

element. In order to regenerate the DPF using the electrical heating system, it was 

necessary to bring the vehicle to the shop and connect the heater to shore power and 

connect a source of compressed air to the inlet cone. This was initially planned to 

regenerate the filter at the end of each shift. This was an inconvenient requirement 

opposed by mine production crews. Initially, the electrical regeneration system caused 

considerable technical and safety (electrical fault) problems. During the project it became 

apparent that the platinum catalyzed filter was able to passively regenerate over the duty 

cycle. The electrical regeneration system was thus deemed redundant. The filter system 

performed well over 4260 hours at 99% filtration efficiency of elemental carbon 

particles. 

Oberland Mangold Octel Filter 

This filter utilized cartridges with knitted fiberglass filter media. Filter regeneration was 

facilitated using the same Fe/Sr fuel additive used for the ECS Octel DPF system. 

The first installed version of the filter was undersized in design, causing backpressure 

problems. After it was replaced by a larger unit, the filter performed well. The most 

significant problem with this system was perhaps the large size of the unit, making it 

difficult to install on the vehicle. During the project the manufacturer abandoned the fiber 

cartridge design and it is no longer available on the market. 
- 11 - 

Conclusions 

The project demonstrated that all tested DPFs were able to provide over 90% reduction in 

the DPM mass emissions, as well as reductions in other emissions and in ambient DPM 

exposures, although the ECS Octel filter was unable to sustain this filtration over time. 

It was emphasized that the DPF selection process is a critical factor in successful 

implementation. Requirements for filter regeneration must be covered in the application 

engineering in the beginning and maintenance and operation requirements must be agreed 

upon by all parties for acceptance of the system. The study showed that current off-theshelf DPF technology requires additional custom application engineering in order to be 

optimized for the each individual application. Careful application engineering is needed 

in every individual case. 

The Isolated Zone Study conducted mid-way through the project examined the capability 

of the DPF technologies to meet proposed and existing regulation limits for ambient 

diesel particulate matter concentrations in an actual underground operating environment. 

With more than 2000 operating hours on the systems, all with the exception of the one 

failed DPF demonstrated concentrations near 0.05 mg/m3

 whereas the baseline non-DPF 

vehicles in the study were as high as 0.40 mg/m3. Upon completion of the field study the 

four DPF systems were sent to NRCan CANMET’s diesel certification laboratory for 

final bench testing with laboratory instrumentation and ISO certified procedures in 

parallel to instrumentation used in the field. The final validated performance results for 

gaseous and particulate emissions were combined with a post-bench test inspection and 

autopsy at the laboratory to conclude testing and evaluations. 

The final report contains a wealth of conclusions and recommendations on underground 

application of DPF systems. Ultimately, the success in implementing DPF technology in 

an underground mine comes down to the process and team that a mine puts together in 

selecting, installing, measuring, maintaining, and verifying the systems to ensure longterm performance. 
- 12 - 

IINNTTTRRROOODDDUUUCCCTTTIIOOONNN TTOOO RREEESSSEEEAAARRRCCCHHH

Background

In 1998 the Diesel Emissions Evaluation Program (DEEP) recognized the need for 

technology with the potential to greatly reduce particulate matter emissions from dieselpowered underground mining equipment. DEEP decided to investigate and evaluate 

technologies capable of reducing diesel particulate matter (DPM) by more than 90%, and 

help the industry to radically reduce exposure of underground miners to DPM. At that 

time diesel particulate filter (DPF) technology appeared to be the relatively mature and 

advanced to be implemented on the underground mining equipment. Various DPF 

systems had been evaluated in underground mines since the 1980’s but had limited 

success due to problems with cleaning trapped soot from the filter body. However at the 

time this study was conceived, a joint research program conducted in Switzerland, 

Germany and Austria under sponsorship of VERT extensively field tested several new 

DPF systems and found them suitable for on-road, construction and tunneling 

applications [Mayer et al. 1999]. Those tests showed encouraging results on efficiency 

and durability of the tested systems. Both passive and active technologies were capable of 

regenerating reliably at much lower exhaust temperatures than previously demonstrated. 

DEEP engaged Andreas Mayer, one of the key persons on the VERT program, to assist in 

developing two major in-mine DPF evaluation studies. Noranda’s Brunswick Mine and 

INCO’s Stobie mine were selected to host the studies. The objective of these studies was 

to evaluate the potential of current DPF technology to reduce concentrations of DPM in 

Canadian underground mines by at least 90%. Shortly after, DEEP accepted a project 

proposal from Noranda Technology Center for conducting one of the tests at Brunswick 

Mine. The preliminary work on the project started in the first quarter of 2000. Four 

different combinations of DPFs and vehicles used in underground mine production were 

investigated as potential candidates for the study. 

Project Objectives

The primary objectives of this project were to determine the effectiveness and suitability 

of current DPF technology for controlling DPM emissions from heavy-duty underground 

mining vehicles. A part of this objective was to investigate feasibility of implementing 

this technology in underground environment. The field evaluation of DPF systems was 

conducted in the underground mine at Noranda’s Brunswick Mine in Bathurst, New 

Brunswick. After completion of the field study, the systems were removed from the 

vehicles and bench tested at the CANMET diesel testing laboratory in Bells Corners, 

Ontario 

The following aims were established in order to accomplish this objective: 
- 13 - 

1. Establish a methodology for selecting DPF systems for underground mining 

vehicles, using information on vehicle duty cycle, and DPF and mine 

characteristics. Apply the methodology to select DPF systems for targeted 

vehicles at Brunswick Mine ; 

2. Determine the efficiency of selected DPF systems in controlling DPM emissions 

from underground mining diesel-powered vehicles; 

2.1. Measure the effectiveness of the selected DPF systems in reducing 

concentrations of DPM in tailpipe of tested vehicles 

2.2. Quantify the impact of tested DPF technology on tailpipe concentration of 

CO, NO, NO2, 

2.3. Conduct an isolated zone study to asses the effects of DPF systems on 

concentration of DPM in mine air and personal exposure of the operators 

3. Investigate viability of selected DPF systems for underground mining 

applications with respect to operability, durability, reliability, maintainability, 

and costs; 

4. Develop expertise among Canadian mine personnel, corporate technical and 

OSH personnel, R&D service providers and DPF suppliers, with new DPF and 

emissions measurement technologies. 

Project Scope and Structure

The project was executed in seven stages, within a three-year time span from start to 

finish. Execution of the project required collaboration from many organizations and 

individuals from Noranda Technology Centre, Brunswick Mine, engine, vehicle and DPF 

manufacturers, fuel and additive companies, and research organizations from Canada, the 

United States, and Switzerland. 

Project Stage 1: Preliminary Work 

This preliminary stage involved identifying and allocating the human resources, test 

vehicles, test equipment, instrumentation and tools needed for the project. The most 

significant deliverable in this stage was establishing exhaust temperature and 

backpressure profiles for the mine vehicles selected to be outfitted with DPFs, as a 

preliminary step for selecting DPF test systems. 

Project Stage 2: Characterization and Selection 

At this stage the project team generated a request for proposals (RFP). The RFP was used 

to solicit proposals from several DPF manufacturers. The RFP sought four distinct DPF 

systems that would be fitted on selected mine vehicles and tested over a period of 4000 

operating hours. Established temperature profiles along with specifications for engines, 

vehicles and mine operation were provided to the DPF manufacturers to assist them in the 

process of selection and optimization of DPF systems for candidate vehicles. 

Project Stage 3: Selection, Installation and Training – Implementation 

Four DPF systems were selected between those proposed. The DPF systems were 

installed by mine mechanics with help from the DPF manufacturers. DPF manufacturers 
- 14 - 

provided training to the mine maintenance people on how to operate and maintain the 

systems. Technical representatives from DPF manufacturers were also present during the 

initial baseline emissions tests. Within the first three months of the installation 

manufacturers provided extensive technical support to the maintenance personnel at the 

mine. 

Project Stage 4: Long Term Evaluations of DPF Performance 

Elaborate measurements of DPM and gaseous emissions from the vehicles equipped with 

DPFs were conducted four times during the field evaluation portion of the study. Several 

different instruments were used to monitor emissions, engine, and DPF performance. 

These instruments are described in more detail later in the report. During the extent of the 

study performance of the systems was closely monitored and recorded. This data base 

was used to assess durability, reliability, and viability of the systems 

Project Stage 5: Short Term Evaluation of DPF Systems in an Isolated Zone 

The vehicles equipped with DPF systems were operated in production often in the 

presence of other diesel vehicles. Under such conditions it was not possible to accurately 

assess the impact of the DPF systems on ambient concentrations of DPM and on the 

exposure of vehicle operators to DPM. Therefore, it was necessary to arrange a shortterm study with objective to assess the effects of DPF systems on air quality in the mine 

and miners exposure to DPM. For that purpose a zone of the mine was isolated from 

other parts of the mine where diesel-powered vehicles were operated. The zone was 

ventilated with fresh air supplied directly from fresh ventilation shaft. The vehicles 

equipped with filters and two other vehicles equipped with diesel oxidation catalysts were 

tested in the isolated zone. 

Project Stage 6: Laboratory Emissions Testing and Inspection 

After the completion of in-mine testing, the DPF systems were removed from the 

vehicles and sent to CANMET’s Bells Corners engine and emissions testing laboratories 

for bench testing and for identification of mechanical failures and defects. 

Project Stage 7: Data Consolidation and Final Report 

A significant amount of data was generated through 4000 hours of field testing as well as 

through bench testing and inspections. The essential data and findings are summarized in 

the body of the report. 

DPF Selection Process and Methodology

Considerable effort was invested into selecting the most suitable technologies for the 

applications considered in this project. A comprehensive request for proposal (RFP) was 

compiled and sent to manufacturers of DPF technologies in Canada, the United States 

and Europe. The RFP contained detailed information on the mine and operations, and on 

the engines, power trains, exhaust temperature and backpressure profiles collected for the 

test vehicles. Manufacturers were invited to submit written proposals, and to present them 

at a DEEP Technical Committee meeting a few months later. The final selection of 
- 15 - 

systems was made following consultations between the project leader, Brunswick Mine 

management, and the DEEP Technical Committee. 

Specifications For Selected Vehicles and Mine Application 

Four DPF systems installed on four heavy-duty production vehicles were tested during 

this study. Two of the vehicles were load-haul-dump (LHD) vehicles (Atlas Copco, 

Model ST8-B Scooptrams®®®) similar to the one shown in Figure 1. The LHD is a multifunctional vehicle that operates as a front-end loader to dig into a muck pile, carry the 

load to a dump transfer point and then return to the load point to repeat the cycle. The 

technical specifications for the LHDs are shown in Table 1. The other two vehicles used 

in this study were haulage trucks (Atlas Copco, Model MT436-B) similar to the one 

shown in Figure 2. These machines are designed to haul large loads over longer distances 

and would be typically loaded either by a LHD or by an overhead chute. The technical 

specifications for those trucks are given in Table 2. 

At Brunswick Mine these two types of vehicles are the backbone of the ore transportation 

process. The broken ore is drawn from an open stope by the LHDs. The haul distance 

from the draw point of the stope to the truck loading point or the ore pass is kept to a 

minimum, generally within one to two minutes haul time. At the dump point, the LHD 

would transfer the ore to the dump box of the haulage truck. Loading of the truck is 

usually completed in two buckets. The truck will haul the load to an ore pass (a vertical 

chute that transfers ore to a crusher at the bottom of the mine). The haulage distance from 

loading to dump points for the trucks will vary depending on the area, but is typically 

several minutes. While the truck is away on a haul cycle the LHD will load another 

bucket and wait for the truck to return. In cases where the distance between the stope 

draw point and ore pass is close, the LHD will load, haul and dump ore directly 

bypassing the need for a truck. 

The mine production and maintenance operations work on a two shifts per day basis. 

Both day and night shifts start at 7:00 and finish at 5:30. This leaves a 2 1⁄2 hour window 

between shifts twice per day. The mine operates seven days a week. Mine production 

vehicles normally accumulate about 250 operating hours per month. 
- 16 - 

Table 1 - Atlas Copco Wagner ST8B Scooptram®®® Specifications

ENGINE 

Detroit Diesel Series 60 

Power Rating 242 kW (325 HP) @ 2100 RPM 

Maximum Torque 1559 Nm (1150 ft-lbs) @ 1200 RPM 

Cylinders 6 In-Line 

Displacement 11.1 Liter (677 in3) 

Cooling Water 

Exhaust Flow @ Rated Speed 57.8 m3/min (2040 CFM ) 

Exhaust Flow @ Peak Torque 35.4 m3/min (1250 CFM ) 

Exhaust Temperature @ Rated Speed 321 oC (610 oF) 

Exhaust Temperature @ Peak Torque 521 oC (970 oF ) 

MSHA 30 CFR Part 7 Ventilation Rate 510 m3/min (18000 CFM) 

CSA Ventilation (0.05 % sulphur/fuel) 623 m3/min (22000 CFM) 

 

VEHICLE

Fuel Tank 379 Liters (105 gallon) 

Torque Converter Clark C-8000 Single Stage 

Transmission Clark 5000 Modulated Power Shift 

Vehicle Speeds 1st 2nd 3rd 4th 

 5.3 9.0 15.1 24.6 (km/hr) 

Tramming Capacity 13608 kg (30000 lbs) 

Operating Weight (Empty Approximately) 39474 kg (87,040 lbs) 

Figure 1 - Atlas Copco Wagner ST8B Scooptram®®®
- 17 - 

Table 2 - Atlas Copco Wagner MT436B Haulage Truck Specifications

ENGINE 

Detroit Diesel Series 60 

Power Rating 278 kW (375 HP) @ 2100 RPM 

Maximum Torque 1763 Nm (1300 ft-lbs) @ 1200 RPM 

Cylinders 6 In Line 

Displacement 12.7 Liter (775 in3) 

Cooling Water 

Exhaust Flow @ Rated Speed 66 m3/min (2330 CFM ) 

Exhaust Flow @ Peak Torque 42.2 m3/min (1490 CFM ) 

Exhaust Temperature @ Rated Speed 371 oC (700 oF ) 

Exhaust Temperature @ Peak Torque 504 oC (940 oF ) 

MSHA CFR 30 Part 7 Ventilation Rate 623 m3/min (22000 CFM) 

CSA Ventilation (0.05 % sulphur/fuel) 744.7 m3/min (26300 CFM) 

 

VEHICLE

Fuel Tank 439 Liters (116 gallon) 

Torque Converter Clark CL-6000 Single Stage with Lockup 

Transmission Clark 6000 Full Power Shift 

Vehicle Speeds 1st 2nd 3rd 4th 

 4.8 8.4 14.0 23.0 (km/hr) 

Payload 32659 kg (72000 lbs) 

Operating Weight (Empty Approximately) 31298 kg (69000 lbs) 

Figure 2 – Atlas Copco Wagner MT436-B Haulage Truck
- 18 - 

Datalogging – Vehicle Duty Cycles 

The four vehicles were outfitted with datalogging systems from Nothiger Electronic in 

Switzerland. The systems are similar to those used in the VERT program [Mayer et al. 

1999]. The dataloggers consisted of display, processor, memory, alarm and 

communication download systems. The dataloggers were coupled with RTD temperature 

sensors, differential pressure sensor, and programmed to record engine backpressure and 

exhaust temperatures. The loggers were used in the preliminary phase of the project to 

acquire data on the duty cycles of the tested vehicles needed for the selection and 

acquisition process. The loggers were also used for long term monitoring of the DPF 

systems once they were installed on the vehicles. 

These duty cycle parameters allowed manufacturers to select and optimize DPF systems 

for the applications with respect to the exhaust temperatures and other features of vehicle 

operation. Figures 3 and 4 show a portion of the data that was presented to the DPF 

manufacturers. The traces in red at the top of the charts are exhaust temperatures from 

two points on the exhaust system and the blue trace at the bottom is exhaust 

backpressure. The chart in figure 3 demonstrates the short tight cycles with high exhaust 

temperatures typical of the LHD application. The chart in figure 4 shows the longer 

cycles with lower exhaust temperatures typical of the haulage truck application. 

Figure 3 - ST8-B Scooptram® Duty Cycle 
- 19 - 

Figure 4 - MT436-B Truck Duty Cycle 

DPF Evaluation Methodology

Tested DPF systems were evaluated on the basis of the quantitative and qualitative data 

collected during field and laboratory studies. Quantitative information on performance of 

the DPF systems were gathered through periodic measurements of tailpipe emissions, 

ambient concentrations, exhaust temperature, and engine backpressure. The data on the 

costs and labor requirements related to acquisition, installation, and operation of DPF 

systems were also recorded. Qualitative information was gathered through field 

communication and meetings with operators, mechanics and mine management. 

Quantitative Evaluation 

The following parameters were measured quantitatively: 

1. Tailpipe emissions 

2. Concentrations of particulate matter and gases in ambient air 

3. Vehicle and DPF operating data. 

Tailpipe Emissions 

The mine maintenance mechanics used rough and ready instruments for day-to-day 

monitoring of tailpipe emissions. The research team used more sophisticated and accurate 

instruments during detailed measurements at periodic evaluations. The tailpipe emissions 
- 20 - 

were measured using the Undiluted Gas Analysis System (UGAS) [McGinn et al. 1998, 

McGinn 2000], the NanoMet diesel particulate characterization system [Kasper et al. 

2001], and a new system developed during this project to measure DPM mass 

concentration in undiluted exhaust. 

UGAS and Bacharach Smoke Density Tests 

The UGAS system was originally developed by Noranda Technology Centre, to support 

emissions assisted maintenance programs at Noranda mines [McGinn et al. 1998]. Since 

then the system was made commercially available by Ecom America Ltd., Norcross, 

Georgia. This system was used by mine maintenance staff as a day-to-day tool to 

evaluate DPF and engine performance. The system is based on the Ecom AC emissions 

analyzer, UGAS software, and a testing protocol integrated into the software. The system 

is designed to measure gaseous emissions listed in Table 3. In addition, the Ecom 

analyzer is designed to draw a 1.6 liter sample of exhaust through a paper filter. The 

collected sample is used for Bacharach Smoke Density Test. The number is assigned to 

the sample after comparing a color of the smoke dot on the sampling filter to a 0 – 9 grey 

scale. Mechanics used this instrument to find soot density at both the inlet and outlet 

sides of the DPF. The smoke numbers were used to roughly assess filtration efficiency of 

tested DPF systems. The measurements with the UGAS system were made by the 

mechanical department at Brunswick Mine during 250-hour monthly inspections and 

occasionally for diagnostics in between inspections. 

Table 3 - ECOM AC Gas Analyzer Parameters

Measured Parameters Range Accuracy Resolution 

Oxygen (O2) 0 - 21% 2% of reading 0.1% 

Carbon Monoxide (CO) 0 - 4000 ppm 4% of reading 1 ppm 

Nitric Oxide (NO) 0 - 4000 ppm 4% of reading 1 ppm 

Nitrogen Dioxide 0 - 500 ppm 4% of reading 1 ppm 

Ambient Temperature 0 - 250° F 3 degrees 1° F 

Gas Temperature 0 - 1600° F 3 degrees 1° F 

Gas Draft (Pressure) 0 - 40.0” H2O 2% of reading 0.01” H2O 

Calculated Parameters Range Resolution 

Combustion Efficiency 0 - 100% 1.0% 

Carbon Dioxide (CO2) 0 - 40% 0.1% 

Lambda (λ) 0 - 50% 0.01% 

Losses 0 - 100% 1.0% 

O2 Correction 0 - 10,000 ppm 1 ppm 
- 21 - 

Figure 5 - UGAS Emissions Testing System

NanoMet Diesel Particulate Measurement System 

The NanoMet Diesel Particulate Measurement System (Matter Engineering AG, Wohlen, 

Switzerland) shown in Figure 6 was acquired by CANMET for the purpose of conducting 

periodic assessments of performance of diesel particulate filters. Although sold as a 

portable field instrument, the NanoMet is essentially a laboratory grade instrument 

modified for field measurements [Kasper et al. 2001]. The NanoMet was found to be a 

sophisticated but complex instrument that required a trained operator. 

The NanoMet system is comprised of: 

 Diffusion Charging Particle Sensor LQ 1-DC (DC) 

 Real time PAH Monitor PAS 2000 (PAS 2000) 

 Spinning disk diluter MD19-2E 

 Heated 3-way sampling interface 

 Software sampling and testing interface 

The two heated sampling lines were used to connect the instrument to the inlet and outlet 

sides of the DPF. The exhaust samples from each of the sampling locations were routed 

alternately to the dilution head and sensing instrumentation using a three way valve. The 
- 22 - 

diluter is also heated. Heated sampling combined with heated dilution prevents volatile 

exhaust components from nucleating and condensing to form nanoparticles and 

interfering with the sample. 

The combination of the two sensors with the heated sampling and dilution permits 

differentiation between solid and liquid fraction of the sampled aerosols. The diffusion 

charging particle sensor uses corona discharge to non-selectively charge solid and liquid 

aerosols. The instrument characterizes the particles in terms of the active surface. The 

PAS 2000 is a photoelectric real-time aerosol sensor. The aerosol is photo charged at the 

inlet to the sensor using an exciter lamp. Since only aerosols with solid core can be 

efficiently charged using photoemission there is belief that the output of the instrument is 

strongly correlated to the elemental carbon (EC) fraction in the DPM samples. The 

instrument has quick response time and wide particle size range. The PAS 2000 proved to 

be a more reliable and consistent instrument for assessing penetration and filtration 

efficiency of the DPF systems than the DC. No absolute values of particle concentrations 

were acquired in the testing with the Nanomet and calculations of filtration efficiencies 

were based only on the PAS 2000 values. 

Figure 6 - NanoMet Diesel Particulate Analysis System

Bacharach Smoke Tests 

The Ecom AC emission analyzer was used to draw exhaust samples upstream and 

downstream of the tested DPF for the Bacharach Smoke Test. During the tests 1.6 litres 

of exhaust was sampled through a circular paper filter inserted into the sampling probe. 

During this test the sampling head in the probe is electrically heated to prevent 
- 23 - 

condensation. The soot concentration spot collected on the paper disc is compared against 

a 0 – 9 gray scale for and index value of soot or particulate concentration. 

Carbon Content of Tailpipe Samples 

A novel method for measurement of tailpipe concentrations of carbon fraction of diesel 

particulates was developed at the early stages of this project. The samples for carbon 

analysis were collected using a Bacharach Smoke Test option of the ECOM AC 

emissions analyzer. The instrument was used to draw 1.6 litres of exhaust sample through 

a filter inserted into the sample probe. The standard paper filter used for smoke number 

tests was replaced with quartz fibre filter capable of sustaining high temperatures 

occurring during carbon analysis using NIOSH 5040. The samples were analyzed by 

CANMET’s laboratory using NIOSH Analytical Method 5040 [NIOSH Manual for 

Analytical Methods, 1999]. This test method was applied to almost all of the interim 

evaluations performed during the project, and provided data to compare to the NanoMet 

and UGAS results. 

Ambient Diesel Particulate Concentrations 

The original intent was to have Brunswick Mine personnel conduct monthly or quarterly 

ambient DPM sampling in the areas where the vehicles equipped with tested DPF 

systems were operated. Unfortunately, local constraints at the mine resulted in more 

sporadic sampling than initially planned. Sampling was conducted by a summer student 

during the spring and summer months of 2000. The focus was on the four tested vehicles. 

Results of the sampling campaign conducted in the summer of 2000 produced 

inconclusive results mostly due to the interferences caused primarily by presence of the 

other than tested diesel-powered vehicles in the sampling zone. 

The more rigorous tests were conducted during the isolated zone study at the mid point of 

the project. These tests were conducted in a controlled experiment environment in order 

to eliminate all potential sources of interference. Only the results on ambient 

concentrations of carbon that were obtained during the isolated zone study were 

discussed in this report. 

All samples collected during preliminary studies and isolated zone study were analyzed at 

CANMET’s laboratories in Sudbury, Ontario, using both the Respirable Combustible 

Dust (RCD) method [Grenier et al. 1996] and the NIOSH 5040 method [NIOSH Manual 

for Analytical Methods, 1999]. 

The samples for Respirable Combustible Dust (RCD) analysis were collected using a 

sampling train consisting of a pre-separator cyclone (10mm York), 37 mm filter cassette 

with silver membrane filter (Gelman), tubing, and a calibrated constant flow sampling 

pump set to 1.7 litres per minute (Gilian). 
- 24 - 

Gravimetric determination and analysis involves weighing the silver membrane filter 

before and after an ashing (burning) process which yields the mass of the estimated diesel 

particulate matter (DPM) defined as RCD. This method has a high detection limit at or 

about 0.6 mg/m3 and interference related limitations. Analysis results can be 

overestimated due to interference from cigarettes, drill oil mists or other sources of 

carbon. Similarly, results can also be underestimated in mines where high sulphide 

mineral dusts are present. With resolution or compensation for interference factors the 

RCD method is simple and inexpensive and accurate in RCD mass sample analysis > 

0.60 mg/m3 [Grenier et al. 2001]. 

The NIOSH 5040 method [NIOSH Manual for Analytical Methods, 1999] uses the same 

sampling train as above except for the addition of a size impactor between the cyclone 

and cassette to block particles greater than 0.8 microns, the usual cutoff point for diesel 

and non-diesel particles. The sampling pump for this method is calibrated to 2 litres per 

minute. Samples are acquired on quartz-fiber filters in the cassettes. Analysis is 

performed at a laboratory by first using a punch to remove a 1.5 cm2

 cutout from the 

sample filter. The cutout is analyzed with an instrument that uses temperature and 

atmosphere control while measuring optical transmittance of the sample. Analysis is done 

in two stages with speciation of organic and elemental carbon defining a “split” between 

the two as shown in figure 8. The first stage of the analysis defines organic carbon 

evolved in a helium atmosphere at a temperature stepped to 850° C. The second stage 

defines the elemental carbon split with an oxygen-helium atmosphere at a temperature 

stepped to 940° C. This is the same analysis method used to calculate the values from the 

undiluted samples with the Ecom probe mentioned in the previous section. 

Figure 7 - RCD and NIOSH 5040 Operator DPM Sampling Trains 
- 25 - 

Figure 8 - Method 5040 Analysis Example

Vehicle and DPF Operating Statistics 

Throughout the field study, the operational parameters on the tested vehicles, engines, 

and DPF systems were monitored to determine how the vehicles were operated and 

whether the DPFs were able to regularly regenerate. Two data acquisition systems were 

used to acquire this data. 

The four vehicles used in this study were powered with Detroit Diesel electronically 

controlled (DDEC) engines. The engine control module (ECM) computer onboard the 

tested vehicles provided data on operating hours, idling hours, fuel consumption, and 

engine operating profiles with incremental engine speeds and loads over test periods (see 

Figure 9). This data proved to be the very valuable and accurate for establishing 

operating trends on the tested vehicles. 
- 26 - 

Figure 9 - DDEC Reports Engine Operating Statistics 

The Nothiger dataloggers were also used to continuously collect selected data on 

performance of DPF systems. The information from the exhaust temperature and 

backpressure sensors was used to establish filter regeneration frequency. However, these 

instruments proved to have very poor reliability and required more maintenance than any 

of the actual DPF systems tested in the project. Instruments failures resulted in 

significant gaps in the database. The high failure rate meant that loggers and sensors had 

to be changed at frequent intervals. There were significant gaps in time where failed 

hardware went undetected and no data was acquired. 

Qualitative Evaluation 

From the beginning of the project, the research team assumed qualitative results would be 

relatively easy to acquire. Researchers planned to log written feedback from vehicle 

operators, mechanics and maintenance people, and mine management. Log books left 

with the vehicles were not well received and left empty as was a subsequent plan to set 

up a voice mail feedback phone extension at the mine. In the end, feedback was largely 

obtained through informal discussions with operators, mechanics, and management. The 

project leader was able to spend a significant amount of time underground at the mine 

over the course of the project and during this time, had many discussions with all mine 

employees associated with operating, maintaining and implementing the DPF systems. 

These interviews and discussions were recorded in hand written notes. 
- 27 - 

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AAPPPPPLLLIIICCCAAATTTIIIOONNSS AAANNNDDD SSPPPEEECCCIIIFFFIIICCCAAATTTIIOONNNSSS

Proposals and Selection

In September, 1999 the Request for Proposal (RFP) was sent out to more than twenty 

manufacturers of diesel particulate filter systems and related technologies such as fuel 

additives and filter media. The RFP was appended with contract documents that 

contained terms and conditions for participation in the project and detailed design and 

performance targets. The targets addressed size and weight of the system, minimum 

required filtration efficiency, maximum exhaust engine backpressure, limitations on 

service effort and cleaning, and expected life of DPF technologies to be tested. The 

manufacturers were requested to submit their proposals by a given date. They had an 

option to present their proposals at a joint meeting involving the DEEP Technical 

Committee, Brunswick Mine representatives, and the other manufacturers. 

Only four manufacturers responded to the RFP and between them, came forth with a total 

of eight proposals or iterations. Engine Control Systems (ECS) of Toronto, Ontario 

presented three proposals, DCL International of Toronto, Ontario presented two 

proposals, Nett Technologies of Toronto, Ontario presented two options, and Oberland 

Mangold GMBH of Germany presented one proposal. 

The four systems for the test vehicles were selected by Brunswick Mine representatives, 

the DEEP Technical Committee, and the project leader. Selection criteria were 

established taking into consideration reliability, viability and technical sophistication of 

the systems. From the research perspective the objective was to select DPF systems that 

are representative of the most advanced technologies available at the time. From the mine 

operation perspective the objective was to select technologies that could reasonably be 

accepted by mine operations and maintenance beyond the project should they prove 

successful. 

One of the DPF systems presented by Engine Control Systems (ECS) was chosen for one 

of the LHD applications. The design was selected because of its simplicity and proven 

reliability. Two ceramic Cordierite EX-80 monoliths as shown in Figure 10 were 

mounted horizontally between inlet and outlet manifolds of the DPF system. Ceramic 

filter monolith technology from Corning has been proven to be durable in use in mines 

since the 1980’s. To secure regeneration of the DPF elements during the duty cycle of the 

LHD the monoliths were wash coated with a base metal catalyst. The coating was 

designed to lower regeneration temperatures without increasing gaseous emissions, in 

particular NO2. The system was designed as a fully passive system. The regeneration of 

the system should occur during the typical LHD operating cycle and was completely 

transparent from the operator’s perspective. ECS assigned the product name of CatTrap 

to the system and to which it is herein referred in this report. 
- 28 - 

Figure 10 - ECS CatTrap Ceramic Monoliths

A second system proposed by ECS was chosen for application on an MT-436B truck. 

The DPF system shown in Figure 11 was a modified ECS Unikat Combifilter design 

which used twin K18 silicon carbide filter monoliths and canisters, but substituted a 

catalytic converter (DOC) above each monolith section instead of the electric heater 

assemblies normally mounted in the upstream housings. The silicon carbide monolith 

technology has a proven track record for durability and higher resistance to thermal stress 

than Cordierite ceramic materials. A fuel-borne catalyst was used with the system to 

ensure regeneration of filter elements at the lower exhaust temperatures characteristic of 

relatively cold duty cycles observed for the haul trucks. The fuel-borne catalyst was 

supplied by Associated Octel Limited under the product name of Octimax 4804. The 

active components of this catalyst are iron and strontium. The product was proven 

through the research projects conducted in Europe [Vincent et al. 2000]. 

Figure 11 - ECS Octel DPF Components
- 29 - 

A DPF system proposed by DCL International was chosen and adopted for retrofit on the 

other LHD vehicle included in the research. The system was chosen as a test of a 

promising active DPF technology that could reasonably fit within the constraints of 

Brunswick Mine operation requirements. This DPF system was designed around a single 

silicon carbide filter monolith. The monolith was wash coated with a platinum catalyst. 

An active electric heating system was added to the system to ensure DPF regeneration. 

This system had a 600-volt electrical element as shown in Figure 12 mounted in the inlet 

cone of the DPF housing. A regeneration station with the electrical power supply, 

switches, and controls and compressed air connections was designed as a separate unit 

external to the vehicle. The system was designed to be electrically regenerated at the end 

of each shift. The regeneration station was located in the garage on 3250 level. The plan 

was to have the operator(s) bring the vehicle to the garage at the end of each shift where 

the DPF system would be connected to the regeneration station. The two and a half hour 

window between work shifts was found to be sufficient to complete the regeneration 

cycle. The DCL system is referred hereinafter under the product name Bluesky. 

Figure 12 - DCL Bluesky DPF Silicon Carbide Monolith and Heater Element

A system proposed by Oberland Mangold of Germany was selected for application on the 

second MT436-B truck. The system used a glass fiber filter technology instead of wall 

flow monoliths of the other tested systems. The glass fiber cartridges had been approved 

by VERT following European tests [Mayer A, 1998]. The system also included a fuelborne catalyst in the design to meet the regeneration requirements of lower exhaust 

temperatures in typical truck duty cycles. Oberland Mangold agreed that the Octimax 

4804 additive would be appropriate for this use. The Oberland Mangold DPF system is 

shown below in Figure 13. 
- 30 - 

Figure 13 - Oberland Mangold DPF Glass Fiber Cartridges

DPF Installations

ECS CORDIERITE DPF ON VL244 ST8-B SCOOPTRAM

The installation of the ECS CatTrap ceramic cordierite DPF system was straightforward. 

The exhaust compartment on VL244 was quite large and could accommodate changes to 

the exhaust system without significant modifications on the vehicle. The installation was 

relatively simple due to fact that the ECS DPF system was similar in physical size to the 

OEM catalytic converter/muffler combination. 

All piping from the turbocharger to the DPF was rebuilt with new elbows, flex pipe and 

band clamps. The DPF was configured with twin canisters mounted horizontally between 

block inlet and outlet manifolds. (See Figure 14) The manifolds were equipped with 

appropriate ports and fittings for connecting backpressure and temperature sensors and 

for emissions analyzers and other instrumentation during tests. The guards and floor 

plates above the trap system were modified slightly to accommodate the change in height 

of the trap system. 

The Nothiger datalogger was installed on the operator side of the vehicle behind the 

mount and guard for the intake filter housing. The box was facing the operator. 

The completed installation took 2 full shifts, with 4 active participants, approximately 64 

total hours of labour in total. 
- 31 - 

Table 4 - ECS CatTrap Installation on VL244 Scooptram

VL244 VEHICLE SPECIFICATIONS

Manufacturer and Model Atlas Copco Wagner – ST8 B Scooptram 

Serial Number DA15PO528 

Air Intake System Dual dry type air cleaners – Donaldson 

ENGINE SPECIFICATIONS

Manufacturer and Model Detroit Diesel Series 60 

Serial Number 6063EK32 – 06RO54727 

Engine Displacement 11.1 liter 

Power Rating 242 kW (325 HP) @ 2100 rpm 

ECM Hours Totals @ Installation 1005 hrs 

ECM Fuel Totals @ Installation 8034 gals 

Fuel Consumption 107.6 lb/hr – 15.4 gal/hr 

Exhaust Flow (rated speed) 57.8 m3/min (2040 ft3/min) 

Exhaust Back Pressure (max) 100 mbar (40 in.wc) 

DPF SPECIFICATIONS

Manufacturer Engine Control Systems (ECS) 

Filter Type Cordierite EX-80 – Catalyzed Base Metal 

Regeneration Passive 

Filter Volume 39.10 liter 

Configuration Twin Canisters with Manifold Horizontally 

Mount 

Retrofit Installation Effort 64 Manhours 

Figure 14 - ECS CatTrap Installation
- 32 - 

DCL SILICON CARBIDE ELECTRIC REGEN DPF ON VL247 ST8-B SCOOPTRAM

The installation of the DCL DPF system was straightforward. The filter was a single 

canister design, not much larger than the original exhaust system. The entire assembly 

was fitted into the exhaust compartment without need for modifications. (See Figure 15) 

The DPF assembly consisted of the platinum catalyzed silicon carbide filter element, a 

600-volt spiral heating coil section, inlet and outlet cone sections, and a short inlet 

extension pipe incorporating a 5” butterfly shutoff valve used during electrical 

regeneration. The installation of the DPF assembly took 3 full shifts. The exhaust piping 

was rebuilt from the turbocharger to the DPF inlet flange. The guards above the exhaust 

did not require any modification. 

The control box for the electrical regeneration station was designed as a separate, 

portable unit on rubber wheels (See Figure 16). The original configuration of the control 

unit had a 600v fused input and disconnect, controls for 600v and 110v systems, pressure 

and flow controls for compressed air, a scanner controller for alarms and controls using 

thermocouples, timer relays, and external control panel and status lights. An umbilical 

cable with the 5 lines connects the control box to the mating parts of the system 

permanently mounted on the vehicle. 

The original plan was to regenerate DPF system in the shop at the end of each shift. The 

regeneration cycle, which was fully automated, would take 90 minutes from start to 

finish. Unfortunately, getting the electrical regeneration system connected and working 

properly presented a significant challenge. Within the first 8 hours of operation, the 

heating element that was designed to preheat the air entering the system failed. The 

investigation revealed that the element was inadequately designed. The preheat element 

was removed from the system leaving only the primary heat coil. This resulted in 

extending the regeneration cycle from 90 minutes to 120 minutes. At the same time two 

thermocouple connections were eliminated for simplicity and robustness. The elimination 

of these connections left only the 600v heating element connection and the compressed 

air connection. These modifications greatly simplified the connection procedure. 

The first test of the regeneration system uncovered more design deficiencies. An 

overheating failure resulted in an electrical short to ground. Lack of ground fault 

protection led to a complete power failure in a large section of the mine. Heat dissipation 

around the on-board electrical controls along with improper connectors and lack of 

ground fault protection all contributed to the failure. Modifications were made by the 

Brunswick Mine electrical department and upon verification and re-testing, the system 

worked very well. 
- 33 - 

Table 5 - DCL Bluesky Installation on VL247 Scooptram 

VL247 VEHICLE SPECIFICATIONS

Manufacturer and Model Detroit Diesel Series 60 

Model – Serial Number 6063EK32 – 06RO576451 

Engine Displacement 11.1 liters 

Power Rating @ 2100 rpm 242 kW (325 HP) 

ECM Hours Totals @ Installation 0.3 hrs 

ECM Fuel Totals @ Installation 0.8 igals 

Fuel Consumption 107.6 lb/hr – 15.4 gal/hr 

Exhaust Flow (rated speed) 57.8 m3/min (2040 ft3/min) 

Exhaust Back Pressure (max) 100 mbar (40 in. wg) 

DPF SPECIFICATIONS

Manufacturer DCL International 

Filter Type Silicon Carbide – Catalyzed Platinum 

Washcoat 

Regeneration Active – On/Off Board Electric 

Filter Volume 34.2 liters (381mm X 300mm) 

Configuration Single Cylinder Horizontal Mount 

Installation Effort 104 Manhours 

Figure 15 - DCL Bluesky Installation on VL247 
- 34 - 

Figure 16 - DCL Regeneration Plug In Unit

ECS OCTEL SILICON CARBIDE DPF ON VH183 HAULAGE TRUCK

The physical size of the ECS Octel DPF system presented a significant challenge during 

the installation. The system with two canisters mounted vertically was more than double 

size of the factory DOC/muffler combination (See Figure 17). The relatively small 

exhaust compartment required redesigning to accommodate the DPF system. The guards 

and shields around the exhaust compartment were rebuilt. These frame modifications 

accounted for almost 60% of the total installation effort. The piping from the 

turbocharger to the filter was completely reworked. The ports and fittings for the sensors, 

instrumentation and emissions testing equipment were installed along the piping. The 

elbow section at the outlet from the DPF system was also rebuilt. 

Additional preparation work was required to secure a discrete fuel supply for VH183 and 

VH181 with the fuel blended with the Octimax additive. Due to concerns related to the 

potential effects of the fuel borne catalyst on human health it was important to restrict use 

of the blended fuel to the two DPF-equipped trucks. It was necessary to separate the fuel 

supply for these vehicles from the fuel supply for the other vehicles in the mine fleet. 

This was achieved by designating separate fuel tanks for the fuel blended with the 

additive. In order to prevent supplying this fuel to the vehicles that were not equipped 

with DPFs those bulk storage tanks were equipped with a Wiggins quick-disconnect fuel 

fill system. The Wiggins hardware was also installed on the fuel tanks of both trucks. 

This type of the fill system is not compatible with the standard fuel filling systems used at 

the mine. 

The Nothiger datalogger was installed in the operator’s compartment just to the right of 

the dash panel. 

The complete installation took 96 total hours of labour. 
- 35 - 

Table 6 - ECS Octel Installation on VH183 Truck

VEHICLE SPECIFICATIONS

Mfgr and Model Atlas Copco Wagner – MT436B Truck 

Serial DB36PO251 

Air Intake System Dual dry type air cleaners – Donaldson 

ENGINE SPECIFICATIONS

Mfgr and Model Detroit Diesel Series 60 – 12.7 liter 

Serial 60603TK32 – 06RO550588 

Power Rating @ 2100 rpm 375 HP – 278 kW 

ECM Hours Totals @ Installation 293 hrs 

ECM Fuel Totals @ Installation 1382 igals 

Fuel Consumption 123.8 lb/hr – 17.7 gal/hr 

Exhaust Flow (rated speed) 2330 ft3/min – 66 m3/min 

Exhaust Back Pressure (max) 40 iwg – 100 mbar 

DPF SPECIFICATIONS

Manufacturer Engine Control Systems (ECS) 

Filter Element Composition Silicon Carbide with in-line DOC 

Regeneration Fuel Borne Catalyst – Octimax 4804 @400ppm 

Filter Volume 39.10 liter 

Geometric Configuration Twin Canisters with Manifold–Vertical Mount 

Installation Effort 96 Manhours 

Figure 17 - ECS Octel Installation on VH183 
- 36 - 

OBERLAND MANGOLD OCTEL FIBER CARTRIDGE DPF ON VH181 HAULAGE TRUCK

The Oberland Mangold (OM) DPF system was the final of the four installations and 

probably the most straightforward due to both experience gained with installation of the 

other systems, and relative size and simplicity of the system. The DPF assembly was 

similar in dimensions to the factory exhaust system yet still required small modifications 

throughout the installation. The piping on both sides of the DPF had to be rebuilt. Ports 

for the sensors and emissions tests were welded into the new piping before assembly. The 

modifications to the guards and the frame structure were minimal. 

The Wiggins fuel filling hardware identical to the one installed on haulage truck VH183 

was also installed on this truck. This hardware permitted fuelling these two trucks only 

with the blended fuel and at the same time prevented operators from fueling the rest of 

the mobile fleet with blended fuel. 

The Nothiger datalogger was installed in the operator’s compartment just to the right of 

the dash panel. The cables for the RTD temperature sensors were extended to 

accommodate the location of the logger. A condensate trap for the exhaust back pressure 

sensor was installed on the inside of the engine firewall. 

The completed installation took 72 hours of total labour. 

Although the installation went very smoothly, the preliminary tests revealed problems 

with high exhaust backpressure and filter efficiency. Exhaust backpressure measured 

with the new filter in place was 90 mbar (36 in. wc), very close to Detroit Diesel’s 

maximum allowed backpressure of 100 mbar (40 in. wc). The emissions test with UGAS 

showed that high pressure resulted in increased CO emissions. The deep bed filter 

technology with glass fiber cartridges evidently required a great deal of canister volume 

to provide the necessary filtration surface area. The 25-cartridge configuration inside the 

canister appeared to be undersized for the volume of exhaust gases produced by the 

engine. The system was closely monitored for the first few weeks to assess the efficiency 

and relevant performance parameters of the system. 

High exhaust backpressure problems eventually forced the decision to replace the 

original Oberland Mangold system with a larger volume unit. A new system was 

delivered to the mine and installed within two months Figures 19 and 20 show the two 

Oberland Mangold systems. 

The original DPF system accumulated 300 operating hours before removal and 

replacement with the larger volume unit. Figure 18 shows exhaust temperature (red line) 

and backpressure (blue line) traces for the first four days of operation. The exhaust 

backpressure was exceeding 200 mbar(80 in. wc) or twice the engine manufacturers limit 

of 100 mbar (40 in. wc)in the first days of operation. 
- 37 - 

Figure 18 - Exhaust Temperature and Backpressure Traces for First Oberland Mangold DPF

Table 7 - Oberland Mangold DPF System Installated on VH181 Haulage Truck

VEHICLE SPECIFICATIONS

Manufacturer and Model Atlas Copco Wagner – MT436B Truck 

Serial DB36PO247 

Air Intake System Dual dry type air cleaners – Donaldson 

ENGINE SPECIFICATIONS

Manufacturer and Model Detroit Diesel Series 60 

Serial Number 6063GK32 – 06RO471648 

Engine Displacement 12.7 liters 

Power Rating 278 kW (375 HP) @ 2100 rpm 

ECM Hours Totals @ Installation 2265 hrs 

ECM Fuel Totals @ Installation 13185 igals 

Fuel Consumption 123.8 lb/hr – 17.7 gal/hr 

Exhaust Flow (rated speed) 66 m3/min (2330 ft3/min) 

Exhaust Back Pressure (max) 100 mbar (40 in. wc) 

DPF SPECIFICATIONS

Manufacturer Oberland Mangold 

Filter Type Knitted Glass Fibre Cartridges 

Regeneration Fuel Borne Catalyst – Octimax 4804 

@400ppm 

Filter Volume – 1st Filter 25 Cartridges – 23.7 liter 

Filter Volume – 2nd Filter 52 Cartridges – 49.3 liter 

Geometric Configuration Single square canister – horizontal mount 

Installation Effort 72 hours total labour 
- 38 - 

Figure 19 - Original Oberland Mangold DPF Installation

Figure 20 - Final Oberland Mangold DPF Installation 
- 39 - 

INFRASTRUCTURE AND INSTALLATION FOR FUEL BLENDED WITH OCTIMAX 4804

The DPF systems for both haulage trucks, the Unikat and Oberland Mangold DPF’s, 

were designed to regenerate with help of the Octimax 4804 fuel borne catalyst. This 

catalyst was introduced to lower the regeneration temperature for both systems to 

approximately 350°C. The active catalyst components in the Octimax 4804 are organometallic compounds strontium (Sr) and iron (Fe) [Vincent et al. 2000]. The organometallic compounds are mixed with a carrying and dispersing agent. The Octimax 4804 

was blended with the fuel at a concentration of 400 ppm. This concentration yielded an 

actual organo-metallic compound concentration of 20 ppm with a Fe/Sr ratio of 16:4. 

Throughout the twenty months of the project, samples of blended fuel were sent for 

laboratory analysis to verify the Fe/Sr (16:4) ratio. Diesel fuel at Brunswick Mine is 

supplied by Irving Oil as D2 low sulphur mine fuel with maximum sulphur content of 

500 ppm. 

The bulk blending of fuel required an elaborate infrastructure for mixing, storing, and 

distributing blended fuel. It was important to limit use of blended fuel to the vehicles 

equipped with DPF systems. This was due to potential health risks associated with 

emissions of metallic compounds. A discreet bulk fuel supply was required with 

redundant fail-safe mechanisms to ensure that the two DPF equipped haulage trucks were 

the only vehicles capable of filling with the blended fuel. A six-thousand gallon bulk 

storage tank was installed on surface where the Octimax 4804 was added to the fuel at 

concentration of 400 ppm. Blending was done manually. The recommended volume of 

additive was hand poured into the tank during refilling process. The volume of fuel added 

to the tank was measured using a fuel meter. This process was sufficient to secure 

homogeneous mix of the two. Once homogenized, the blend remained in that state thanks 

to the stabilizing agent from the Octimax additive. A set of portable cube reservoirs were 

designated for transport and store blended fuel. Those reservoirs were equipped with a 

discreet fill/evacuation system. The cubes were moved underground to the “1000 level” 

fuel bay by vehicle transport and shaft access. A second bulk fuel tank of three thousand 

gallon capacity was installed at the fuel bay on “1000 level”. Blended fuel from the cubes 

was transferred to this tank. A separate fill pump and nozzle system was installed at 1000 

fuel bay. The system had a Wiggins quick disconnect fuel nozzle connection. The 

matching female quick connect fittings were installed on the two DPF equipped trucks. 

The bulk blending system proved to be very well suited for the application. The 

alternative solution would have been on-board fuel dosing systems that are common in 

automotive applications but not proven for underground mining applications. 
- 40 - 

Figure 21 - Blended Fuel Storage on Surface

Figure 22 - Blended Fuel Storage at 1000 Level
- 41 - 

Baseline Performance Measurements

The baseline emissions and exhaust properties for VL244 were established shortly after 

installation of the ECS CatTrap DPF system. The results are summarized in Table 8. The 

exhaust backpressure with a brand new filter was approximately 60 mbar (24 in. wc) and 

it was very close to the value established for the original exhaust configuration. The 

results showed no increase in NO2 emissions with this base metal catalyzed DPF system. 

The Bacharach smoke index (BSI) measured upstream of the filter was relatively low (3). 

The BSI measured at the outlet of the system was white (0) and indicated low 

concentrations of DPM emitted out of the system. 

Table 8 - Baseline emissions and exhaust properties establish following installation of ECS CatTrap 

DPF system on LHD VL244

INLET OUTLET

Exhaust Back Pressure 60 mbar (24 in. wg) N/A 

Exhaust Temperature 352oC (665oF) 352oC (665oF) 

Carbon Monoxide (CO) 105 ppm 131 ppm 

Carbon Dioxide (CO2) 5.17% 6.23% 

Oxygen (O2) 13.94% 12.5% 

Nitrogen Oxide (NO) 423 ppm 400 ppm 

Nitrogen Dioxide (NO2) 0 ppm 0 ppm 

Oxides of Nitrogen (NOx) 423 ppm 400 ppm 

Bacharach Smoke Index 3 0 

Table 9 - Baseline emissions and exhaust properties establish following installation of DCL Bluesky 

DPF system on LHD VL247

INLET OUTLET

Exhaust Back Pressure 60 mbar (24 in. wg) N/A 

Exhaust Temperature 407oC (765oF) 391oC (735oF) 

Carbon Monoxide (CO) 106 ppm 1 ppm 

Carbon Dioxide (CO2) 8.4% 8.43% 

Oxygen (O2) 9.52% 9.47% 

Nitrogen Oxide (NO) 692 ppm 624 ppm 

Nitrogen Dioxide (NO2) 30 ppm 114 ppm 

Oxides of Nitrogen (NOx) 722 ppm 738 ppm 

Bacharach Smoke Index 7 0 

The baseline emissions and exhaust properties that were measured for VL 247 equipped 

with DCL Bluesky DPF system are shown in Table 9. The exhaust backpressure of 60 

mbar (24 in. wc) with the brand new clean filter element was approximately equal to the 

one measured with the original equipment exhaust configuration. The carbon monoxide 

was not traceable after the filter. This can be attributed to the catalytic action of the 

platinum catalyst washcoat. The near four-fold increase in nitrogen dioxide emissions 

across the filter, most probably, can also be attributed to catalyst action. The BSI was 

found to be 7 upstream and 0 downstream of the system. 
- 42 - 

Table 10 - Baseline emissions and exhaust properties established following installation of ECS Octel 

DPF system on VH183 truck

INLET OUTLET

Exhaust Back Pressure 37 mbar (15 in. wg) N/A 

Exhaust Temperature 429oC (805oF) 370oC (699oF) 

Carbon Monoxide (CO) 88 ppm 62 ppm 

Carbon Dioxide (CO2) 7.28% 7.6% 

Oxygen (O2) 11.09% 10.69% 

Nitrogen Oxide (NO) 732 ppm 777 ppm 

Nitrogen Dioxide (NO2) 28 ppm 14 ppm 

Oxides of Nitrogen (NOx) 760 ppm 791 ppm 

Bacharach Smoke Index 9 1 

The exhaust backpressure measured with the ECS Octel DPF system installed on VH183 

was found to be relatively low at 37 mbar (see Table 10). Carbon monoxide emissions 

were found to be relatively unchanged despite the inline diesel oxidation catalyst installed 

before the filter monolith. The remaining gaseous emissions were found to be relatively 

unaffected by the system. The BSI was 9 at the inlet and a 1 at the outlet of the system. 

Table 11 - Baseline emissions and exhaust properties establish following installation of Oberland 

Mangold DPF system on VH181 truck

INLET OUTLET

Exhaust Back Pressure 90 mbar (36 in. wg) N/A 

Exhaust Temperature 506oC (943oF) 402oC (756oF) 

Carbon Monoxide (CO) 606 ppm 674 ppm 

Carbon Dioxide (CO2) 9.44% 9.12% 

Oxygen (O2) 8.16% 8.58% 

Nitrogen Oxide (NO) 862 ppm 859 ppm 

Nitrogen Dioxide (NO2) 19 ppm 12 ppm 

Oxides of Nitrogen (NOx) 881 ppm 871 ppm 

Bacharach Smoke Index 9 5 

The preliminary measurements made with a brand new clean Oberland Mangold DPF 

system installed on haulage truck VH181 revealed backpressures in excess of 90 mbar 

(36 in. wc). This was found to be relatively high and of concern since the backpressure 

limit was set by the engine manufacturer at 100 mbar (40 in. wc). The high exhaust 

pressure indicated that the system was undersized for the application. 

The results of emission measurements are shown in Table 11. Carbon monoxide 

emissions were found to be unusually high, above 600 ppm. This was attributed to the 

restriction in exhaust system. The other measured gaseous emissions were found to be 

elevated and almost identical upstream and downstream of the DPF system. The high 

BSIs of 9 at the inlet and a 5 at the outlet were unusually high. The hypothesis is that 

combination of high backpressure due to an undersized filter, and a lower efficiency of 

filter media contributed to this. 
- 43 - 

FFIIEEELLLDDD PPEEERRRFFFOOORRRMMMAAANNNCCCEEE EEVVVAAALLLUUUAAATTTIIIOOONNSS

Methods

Throughout the duration of the project the four DPF equipped vehicles were tested and 

monitored with objective of assessing effects of those on particulate and gaseous 

emissions and evaluating suitability of the systems for the selected mining applications. 

In addition to quantitative assessment, viability of the systems was assessed qualitatively 

using the feedback and perception of Brunswick Mine personnel. 

Effects of DPF Systems on Particulate Matter and Gaseous Emissons 

Four different approaches were used during this study to assess the efficiency of the 

systems in controlling particulate emissions. The first method was established emissions 

tests performed by mine mechanics during preventive maintenance (PM) inspections 

scheduled at 250 hour intervals. During these inspections mechanics used the Bacharach 

Smoke index (BSI) option of the ECOM AC analyzer to characterize particulate matter 

(DPM) emissions. The procedures followed during these tests are previously described in 

DPF Evaluation Methodology. The BSI tests were used to establish pass/fail criteria that 

would be used by mechanics for bringing timely decisions related to performance of the 

DPF systems on a day to day basis. 

The second approach was founded on comprehensive field evaluations performed four 

times over the course of the project. During those evaluations the research project team 

conducted several series of emissions tests. The particulate emissions were characterized 

using the NanoMet Diesel Particulate Measurement System [Kasper et al. 2001] and a 

novel carbon analysis method developed for this study. The DPM emissions were 

measured for a set of six engine operating modes. The following modes and sequence 

were established at the start of the project and performed consistently through the four indepth performance evaluations: 

1. Full throttle – Full Torque Converter Stall 

2. Snap Acceleration – Free No Load (Sets of 3) 

3. Snap Acceleration – Full Torque Converter Stall (Sets of 3) 

4. Idle – No Load 

5. Full Throttle – No Load 

6. Full Throttle – Full Torque Converter Stall (The samples for carbon analysis 

method were collected during this mode.) 

The third approach was developed to assess the effects of DPF systems on concentrations 

of particulate matter in mine air and operators exposure to DPM. The initial project plan 

was to use existing operator exposure personal sampling methods and protocols 

established at Brunswick Mine. During the spring and summer of 2000 a summer student 

conducted a sampling campaign. The results from this sampling proved inconclusive due 
- 44 - 

to the abundance of interference factors present during sampling. The vehicles were 

sharing operating environments in varying ventilation conditions and most importantly, 

sharing the ventilation with non-DPF equipped vehicles making the results inconclusive. 

The most conclusive results for ambient PM concentrations were obtained during the 

isolated zone study. These results are presented and discussed in a later section in this 

report. 

The fourth approach was post field study evaluations that were done in the CANMET 

laboratories in Bells Corners, Ontario after the DPF systems were de-commissioned. The 

four systems were sent to the laboratory for testing on a Series 60 engine and 

dynamometer with a wide spectrum of emissions testing performed there. Following the 

laboratory testing the DPF systems were inspected using both destructive and nondestructive testing techniques for final evaluation. These tests and results are presented in 

a later section of this report. 

Regeneration of DPF Systems and Other Operational Issues 

The temperature and pressure traces gathered during this project were used to study 

regeneration processes for the tested DPF systems. Nothiger dataloggers were installed 

on all tested vehicles and used to continuously record exhaust temperatures and 

backpressures. The dataloggers provided accurate, but sporadic data. Frequent failures of 

temperature and backpressure sensors or the logger control units themselves produced 

large gaps in what was hoped to be a continuous set of data. The data outside of these 

gaps remained accurate and was pieced together to study regeneration trends of DPF 

systems. In addition, during the 250 hour PM inspections the Brunswick mine mechanics 

measured exhaust backpressure with mechanical gauges which gave general trends of 

regeneration and plugging of DPF systems. 

Throughout the project feedback and perception on performance of DPF systems was 

sought from Brunswick Mine production operators, mechanics, supervisors and 

management. The procedures involving logbooks and a dedicated telephone line voice 

mail were established but feedback was infrequent. Discussions and interviews between 

the project leader and Brunswick personnel were recorded in field notes and in some 

cases on video tape. 

Results

ECS CatTrap DPF System Installed on LHD VL244

The ECS CatTrap DPF system performed well in all aspects throughout the field study. 

The DPF system was a good match to the LHD application. The system was regenerating 

successfully during the duty cycle therefore backpressure was within the limits prescribed 

by the engine manufacturer for most of the operating hours. The results of all periodic 
- 45 - 

DPM emissions measurements performed during the project showed high filtration 

efficiency of the system measured by smoke number, elemental carbon particle 

concentration and mass. The emissions and resulting concentrations of all measured 

gases including NO2, were well below limits set by New Brunswick regulations [New 

Brunswick, 1996]. The base metal catalyst did not cause any increase in NO2 emissions. 

This passively regenerated system was very well accepted by operators and management. 

An unexpected event mid-way through the field study proved the ruggedness of the 

system. At approximately 2500 operating hours LHD VL244 was buried in a stope cavein while being operated on radio remote. The entire vehicle was buried under rock. The 

rebuild of the vehicle took some four months to complete. The DPF system not only 

survived the burial but also required no repairs. 

Chronology of Events 

 May 2000 - DPF system installed on LHD VL244. At the time of installation the 

vehicle and engine had 1005 operating hours since new. 

 June 2000 – First tailpipe emissions performance evaluation tests 

 November 2000 – The system accumulated 1000 operating hours – The DPF was 

sent to ECS for cleaning and inspection 

 February 2001 – Isolated zone and second tailpipe emissions performance tests 

 May 2001 – The system accumulated 2500 operating hours – The vehicle was 

buried in a stope 

 June 2001 – Missed third performance evaluation tests due to vehicle rebuild 

 August 2001 – Returned to production after rebuild 

 November 2001 – Final performance evaluation tests 

 January 2002 – The system de-commissioned at Brunswick Mine 

o The system accumulated total of 4053 operating hours 

o The vehicle consumed total of 32,000 gallons of fuel during test period 

o The vehicle was operated 22% of total hours at low idle conditions 

 September 2002 – The system was bench tested at CANMET, Bells Corners 

laboratory 

 2003 – The system was tested at Environment Canada laboratories (independent 

of the project) 

 2003 – The system was returned to Brunswick Mine and reinstalled on the vehicle 

for further evaluation 

Exhaust Temperature and Backpressure 

The typical exhaust temperature and backpressure trace for LHD VL244 is shown in 

Figure 23. Temperature peaked between 375° and 400°C. The system manufacturer 

expected that the filter would be successfully regenerating at those temperatures for 30% 

or more of the total duty cycle. Backpressure reached a plateau of around 120 mbar or 50 

inches of water. The backpressure values measured by mechanics at monthly PM 

inspections were consistent with those measured by the loggers. 
- 46 - 

Figure 23 - ECS CatTrap Exhaust Temperature and Backpressure

Gaseous Emissions 

Over the course of the project a total of 16 emissions tests were performed using UGAS 

at both the inlet and outlet of the DPF. The results are shown in Figure 24. The results 

showed that nitrogen dioxide emissions were not substantially affected by the base metal 

catalyst. Carbon monoxide emissions were consistent and correlating well to small 

fluctuations in carbon dioxide. All measured CO2 emissions were near 8 to 9% indicating 

good tests at full engine stall condition. 
- 47 - 

Figure 24 – Gaseous Emissions For VL244 With ECS CatTrap

Diesel Particulate Matter (DPM) Emissions 

The emissions from VH244 equipped with ECS CatTrap were measured at only three out 

of the four in-depth performance evaluation sessions. During the third session the vehicle 

was out of service for overhaul needed after vehicle burial. Results of the three sets of 

tests, shown in Figure 25, showed that filtration efficiencies of the system are higher than 
- 48 - 

95%. The final set of tests conducted in November, 2001 with 3700 hours of operation 

accumulated by the system showed a noticeable decline in filtration efficiency. 

The carbon content test results obtained using 5040 method were found to correlate well 

to the results obtained using the six-mode testing and the NanoMet instrument. 

Figure 25 – DPM Filtration Efficiencies For ECS CatTrap DPF System

The Figure 26 shows the filter sample taken by mechanics with the UGAS using 

Bacharach smoke index (BSI) option.. The black dot represents the DPM sample 

collected from the inlet side of the filter and the light gray dot represents the sample 

collected at the outlet side of the filter. The samples collected at the final tests in 

November 2001 indicate the reduced efficiencies observed with other methods (see 

Figure 25). 
- 49 - 

Figure 26 – Bacharach Smoke Index Measured for ECS CatTrap DPF System

Observations 

Feedback from operators and mechanics regarding the ECS CatTrap system was almost 

always positive. Since VL244 was extensively used in dead-end draw points inside the 

stopes with reduced ventilation flows, operators noticed and greatly appreciated 

reductions in DPM emissions achieved with this unit. For the majority of the time VL244 

was operated remotely from a safety platform situated at the entrance to the stope. 

Typically during this operation the vehicle pushes back the exhaust towards the operator. 

The only negative comment from the operators addressed the additional heat generated 

by the vehicle when equipped with DPF system. The heat-absorbing nature of the DPF 

produced more local heat on the vehicle and the reduced ventilation volumes amplified 

the heat degradation quality of the air. When questioned on this the operators always 

agreed that the reduction in soot was preferred and more than justified the increase in 

heat. 

The maintenance group at Brunswick Mine favoured the ECS CatTrap for the totally 

passive nature of the system. The system did not have extra hardware therefore required 

very little maintenance. The installation of the system was very straightforward and 

simple. This was due to the fact that the system had almost identical dimensions to the 

original exhaust system. This meant that access required to other parts of the vehicle and 

engine needed for servicing and maintenance was not altered by the installation of the 

DPF. 

The mine management appreciated the simplicity and totally passive regeneration of the 

system. From a management perspective, value is often gauged by the benefit presented 

by the technology versus extent of effort needed to make changes in regular practice, and 

additional costs associated with it. The ECS CatTrap represented for management, a high 

efficiency system that worked reliably at a moderate cost, with little to no change 

management resulting from it. 
- 50 - 

DCL Bluesky System Installed On LHD VL247

The DCL Bluesky DPF system performed well according to the majority of the criteria 

set at the onset of the project. However, the on-board active regenerating system with its 

electrical heater and power supply unit created a challenge for the management and 

operators. The system was designed to partially regenerate over the duty cycle. The 

platinum coating on the silicon carbide filter facilitated passive regeneration. The 

regeneration of the system was enhanced using the on-board electrical regeneration 

system. Electrical regeneration required the operators to park the vehicle in a designated 

place at the end of each shift and connect the system to 600 volt electric power. The 

passive regeneration worked better than expected so the requirement for active 

regeneration was reduced. Had the active component been essential to success, the 

system would undoubtedly have failed early in the project. Operators mostly resisted the 

requirement to bring the vehicle to the garage at 1000 level at the end of each shift and 

initiate the active regeneration process. Adherence to this practice was sporadic at best 

throughout the duration of the project. Despite these problems, the system performed well 

throughout the duration of the project. However, during the initial two months of 

operation the system had major technical problems. The original system lacked the 

electrical engineering suitable for an underground mining mobile application. Defects in 

the ground fault protection system, physical mounting and insulation of electrical 

components, and poor quality connections led to a series of failures that almost brought 

an early end to the testing of the system. Collaboration between the electrical and 

mechanical departments at Brunswick Mine brought a quick evaluation, re-engineering, 

and modifications to the system that proved itself for the duration of the project. 

Chronology of Events 

 May 2000 – The system was installed on the VL247 that had 0.5 operating hours 

since new; 

 June 2000 – The first elaborate performance evaluation session; 

 July 2000 – The DPF system was removed from service to make modifications to 

the electrical regeneration system; 

 August 2000 – The system was reinstalled and returned to service 

 October 2000 – The first defective 600 volt heater element was replaced with a 

new one; 

 October 2000 – The insulating blankets were removed due to corrosion problems; 

 February 2001 – Performance of the system was examined during isolated zone 

testing and second performance evaluation session 

 May 2001 – The second 600 volt heater element was replaced with new one; 

 June 2001 – The system was tested during the third performance evaluation 

session; 

 October 2001 – The third 600 volt heater element was replaced with new one; 

 November 2001 – The system was tested during the final performance evaluation 

session; 

 January 2002 – The system was de-commissioned at Brunswick Mine 
- 51 - 

o The system accumulated 4260 operating hours 

o The VH 247 consumed 34,300 gallons of fuel 

o 23% of total hours operating at idle 

 September 2002 – The system was bench tested at CANMET, Bells Corners 

laboratory 

Exhaust Temperature and Backpressure 

The Nothiger datalogger and sensor system used on VL247 to establish time traces of 

exhaust temperature and backpressure was prone to technical problems throughout the 

study. The RTD temperature sensors used at the DPF inlet side were particularly prone to 

failures due to their proximity to the electrical regeneration unit that generated the 

additional heat. Figure 27 shows temporal distribution of exhaust temperature and engine 

backpressure. This data is fairly consistent with corresponding data obtained for the LHD 

VL244. Exhaust temperatures at peak engine load were between 350° and 400° C, These 

temperatures were theoretically within the range of temperatures needed for passive 

regeneration of this system. Backpressures observed with this system were slightly lower 

than those observed for the ECS system on LHD VL244. The backpressure reached a 

plateau at approximately 100 mbar or 40 inches of water. This indicates that regeneration 

was occurring frequently enough during the duty cycle to sustain continuous operation of 

the system. This was verified by the additional measurements of engine backpressure 

done by mechanics during monthly PM inspections. 

Figure 27 - Exhaust temperatures and engine backpressures recorded for LHD VH247 equipped 

with DCL Bluesky DPF system
- 52 - 

Gaseous Emissions 

Results of the emissions measurements conducted during 20 tests are shown in Figure 28. 

The measurements were conducted at the inlet and outlet sides of the DPF using the 

UGAS system. The CO was converted almost completely across the platinum catalyzed 

filter (see Figure 28). In some cases measurements showed that the concentrations of NO2 

at the outlet of the DPF were four fold higher than corresponding concentrations on the 

inlet side of the DPF. These results emphasized the importance of including gaseous 

emissions measurements in tests designed for evaluation of the effects of DPF systems on 

the particulate matter emissions. 

Figure 28 - Gaseous Emissions For VL247 With DCL Bluesky DPF System
- 53 - 

Diesel Particulate Matter (DPM) Emissions 

The results of particulate matter emissions measurements conducted during four detailed 

performance evaluations are shown in Figure 29. In terms of filtration efficiency, this 

system was the best performer of all systems tested in the project. The results were 

consistently indicating filtration efficiencies in excess of 99 percent. The results obtained 

with NanoMet during tests conducted in February of 2001 were found to be inconsistent 

due to instrumentation problems but are presented nonetheless. It is important to note that 

these tests were conducted during the isolated zone study in a drift at ambient air 

temperature just above the freezing point. We believe that the NIOSH 5040 method 

provided accurate results. 

Figure 29 - DPM Filtration Efficiencies For DCL Bluesky DPF System
- 54 - 

Figure 30 shows the filter sample taken by mechanics with the UGAS using the BSI 

option on the Ecom analyzer. The black dots represent the DPM sample collected from 

the exhaust at the inlet side of the filter (an 8 on the 0-9 index scale) and the light gray 

dot represents the DPM sample collected at the outlet from the filter (a 1 on the 0-9 

index). The results of smoke density tests confirmed the results obtained using other more 

sophisticated methods. 

Figure 30 – Bacharach Smoke Density Results on VL247 with DCL Bluseky DPF System

Observations 

After the electrical problems encountered at the beginning of the study were overcome 

the DCL Bluesky system performed well during the rest of the study. The system 

exhibited the highest filtration efficiencies of all systems tested during this project. The 

system was regenerated passively using heat generated by VL247 over its normal duty 

cycles. Therefore, the active regeneration unit that was provided with system and created 

serious problems was redundant. The poor performance and high maintenance 

requirements of the active regeneration system were the major reasons for negative 

feedback and opposition to long-term deployment of the system in the mine. The lack of 

need for active regeneration of the system presented one of reasons that negatively 

affected enforcement of the policy of active regeneration after every shift. Operators did 

not want to make the effort to drive the unit to the garage at the end of each shift to 

connect the system to the regeneration station. Mine management did not want to make 

the commitment to enforce this policy. 

Because of the failures of the regeneration units at the early stages of project the 

mechanical department at Brunswick Mine developed a negative attitude toward to the 

DCL Bluesky system. Replacement of the 600 volt heater coils that was performed three 
- 55 - 

times over the length of the project was a sizeable and dirty job. The mechanics did 

observe and commented on the high filtration efficiency of the unit during emissions tests 

performed at 250-hour intervals. The size of the unit was not an issue for the mechanics. 

The unit did not create additional problems related to vehicle and engine maintenance. 

Management also developed negative attitude toward this system because of the 

problems encountered at the early stages of the project and because of requirements for 

additional work with active regeneration of the system. This system with active 

regeneration was seen by management as a last choice. The similar LHD VL244 had a 

totally passive regeneration system that worked well and there was little incentive for 

management to pursue an active regeneration system. Had this system been tested in an 

application that absolutely required active regeneration, for example in the case of the 

application where heat generated over duty cycle is insufficient for passive regeneration, 

the mine management might have been more receptive to it 

ECS Octel System Installed on VH183 Truck

The ECS Octel DPF system consisted of twin silicon carbide monolith filters mounted 

vertically, with oxidation catalysts above the inlet sides of the filters. The system used 

fuel blended with the Octimax 4804 catalyst. At the early stages of the study, the system 

looked very promising. It offered high filtration efficiency and no backpressure problems. 

Approximately three months in the project, problems with backpressure arose. When the 

system was disassembled for visual inspection and manual cleaning it was observed that 

a large quantity of soot had been accumulated at the inlet face of the filters. The 

accumulated soot was cleaned from the filter elements using compressed air and the 

system re-assembled. At the request of the system manufacturer, the oxidation catalysts 

were modified and moved to the outlet sides of the filters. This was done in an attempt to 

eliminate potential source of soot buildup on the inlet side. Despite this modification, 

backpressure problems continued and little or no successful regenerations occurred in a 

period of several months. Two uncontrolled regenerations occurred six and eight months 

in the project. These uncontrolled regenerations were the cause of the ultimate failure of 

the SiC filter monoliths. During these two events the metal substrate cores of the 

downstream oxidation catalysts were completely melted. The first of these events 

occurred while the vehicle was at the PM service bay undergoing emissions testing with 

the engine under full load. The second uncontrolled regeneration occurred while the truck 

was being driven up the ramp with a full load. At the point of uncontrolled regeneration 

exhaust backpressure was regularly between 200 and 300 mbar (80 in. wc and 120 in. 

wc), up to three times the 100 mbar limit recommended by the engine manufacturer. 

A new set of filters was installed at the ten months point in the project. The melted 

oxidation catalyst cores were removed and the housings left empty in attempt to alleviate 

backpressure problems. However, backpressure continued to be a problem even with the 

new filters, and within two months approached the level of 300 mbar. The filters were 

again cleaned with compressed air. Before the end of the field study, the second set of 

filters also went through uncontrolled regeneration and was permanently damaged. 
- 56 - 

Managing this system provided the mine maintenance and operations people with 

valuable knowledge and understanding of the operational issues and sensitivity of DPF 

systems. Careful and continuous monitoring of the systems was found to be essential for 

success of the installation.

The combination of several factors was found to cause slow and inadequate regeneration 

of the ECS Octel DPF system. The truck VH183 idled for long periods of time while 

waiting to be loaded by LHDs and waiting at orepasses. It was also evident that the 

Octimax fuel borne catalyst did not reduce regeneration temperatures to the extent 

claimed by supplier. There were significant periods when engine exhaust temperatures 

were between 350° and 400°C yet the regeneration did not occur. The design of the DPF 

system itself left many questions regarding sizing, location of oxidation catalysts, and 

exhaust flow and pressure factors that governed heat retention time inside the filter 

media.

Chronology of Events 

 May 2000 – The system was installed, the vehicle had 293 operating hours since 

new 

 June 2000 – The first measurement of DPF performance and efficiency 

 August 2000 – Backpressure problems prompted inspection and cleaning. The 

DOC’s were moved to the outlet side of the filter 

 November 2000 – Uncontrolled regeneration occurred during testing in 3250 shop 

 January 2001 – Uncontrolled regeneration occurred while the truck was climbing 

ramp with full load 

 February 2001 – Isolated zone testing and the second measurements of DPF 

efficiency 

 April 2001 – The system accumulated 2500 hours. The set of damaged filters 

were replaced with new ones 

 June 2001 – The third evaluation of DPF efficiency 

 October 2001 – The third uncontrolled regeneration caused partially the failure of 

2nd set of filters 

 November 2001 – Final evaluation of DPF efficiency 

 January 2002 – The system was de-commissioned at Brunswick Mine 

o 2500 total operating hours on 1st set of DPF filters and 16,000 gallons 

of fuel 

o 1620 total operating hours on 2nd DPF filters and 11,200 gallons of fuel 

o 32.5% of total hours VL183 operated at idle 

 September 2002 – Final bench testing of the system at CANMET, Bells Corners 

laboratory 

Exhaust Temperature and Backpressure 

The backpressure readings acquired from the datalogger correlated well to backpressures 

measured by the mechanics during the monthly preventive maintenance checks. The 

temperature traces shown in Figure 31 indicate that exhaust temperatures were above 

350° C for substantial periods of time The Octimax fuel borne catalyst was advertised to 
- 57 - 

lower DPF regeneration temperatures to approximately 300° C. Therefore, regeneration 

should have occurred more frequently than it was observed.. Figure 31 also shows that 

the backpressures were for a substantial time above 200 mbar and reaching periodically 

even 300 mbar. This high backpressure indicates that the regeneration process was slow 

and insufficient. The Octel representative offered the hypothesis that regeneration did not 

occur over the duty cycle since the moisture content of the soot buildup inside the filter 

monolith was less than expected. Low organic carbon content was hypothesized to be the 

result of efficient combustion inside the electronically controlled engine and operating 

conditions. These factors in combination with excessive engine idle times contributed to 

the insufficient DPF regeneration.

Figure 31 - ECS Octel Exhaust Temperature and Backpressure

Gaseous Emissions 

The results of gaseous emissions in the tailpipe of VH183 equipped with the ECS Octel 

DPF system indicate the problems with this unit. The concentrations of carbon monoxide 

measured in untreated exhaust at the initial stages of the project were ranging between 

300 and 400 ppm. Those concentrations were somewhat higher than those observed for 

the smaller engines used in tested LHDs. As the DPF system was accumulating hours in 

operation and engine backpressure was gradually increasing, CO emissions were 

climbing. Measurements of the inlet to outlet CO emissions through the first ten tests 
- 58 - 

while the diesel oxidation catalyst was in place showed the CO conversion and reduction 

(see Figure 32). Once the diesel oxidation catalyst was removed, CO emissions at the 

outlet were often higher than those at the inlet due to combustion of DPM inside the filter 

while the engine was under full stall testing conditions. Measurable conversion of 

nitrogen oxide to nitrogen dioxide was taking place in the system while the oxidation 

catalyst was in place, but when the catalyst was removed conversion was not measurable.

Figure 32 - Gaseous Emissions For VH183 ECS Octel DPF System
- 59 - 

Diesel Particulate Matter (DPM) Emissions 

The filtration efficiency test results, shown in Figure 33, illustrate the high efficiencies of 

the newly installed system. The tests in February 2001 show a severely failed filter and 

the final tests in November 2001 show a partially failed filter. The results of the 5040 

method carbon content analysis on the samples collected during the last three sets of tests 

correlate very well with the filtration efficiency measured by the NanoMet instrument. 

Test results showed that the new filters had efficiencies of approximately 98%, similar to 

the other tested DPFs. The severely damaged filter system had efficiency as low as 30%, 

and the partially damaged system had efficiency as low as 82% depending on which test 

mode was used for analysis. 

Figure 33 – DPM Filtration Efficiencies for ECS Octel DPF System on VH183 Truck
- 60 - 

The results of the Bacharach Smoke measurements are shown in Figure 34. The BSI 

measurements showed that DPF systems on VH183 failed in two instances. The first set 

of filters failed after 2000 operating hours and the second set of filters failed after 1400 

operating hours. At other test instances when the DPF system was not compromised the 

efficiency was relatively high. These results are in direct correlation with results obtained 

using other more sophisticated methods. Therefore this method is suitable for quick and 

inexpensive verifications of DPF system performance. 

Figure 34 - Bacharach Smoke Density Results on VH183 with ECS Octel DPF System

Observations 

The truck operators did not appreciate the DPF system for a few reasons. The haulage 

trucks generally work in areas with better flow through ventilation than LHDs, and so 

truck operators did not notice the reduction in DPM emissions as much as the LHD 

operators did. The truck operators also did not notice additional heat created by the DPF, 

because the equipment was mounted on the side of the vehicle opposite the operator and 

because the heat was dissipated in the well-ventilated drifts where the drivers work most 

of the time. 

The mechanical maintenance department at Brunswick Mine had mixed feelings about 

the system, either very positive or very negative opinions. The positive comments came 

from mechanics testing the system and witnessing its filtration efficiency in the early part 

of the study. The negative feedback came from those who saw first hand the effects and 

results of uncontrolled regeneration and temperatures high enough to melt the metal 

substrate in the DOC. The most negative feedback came from the mechanics on the PM 

service bay responsible for performing monthly preventive maintenance checks. The size 

of the system presented a significant problem for mechanics performing work on the 
- 61 - 

engine. Work on the engine was virtually impossible while the engine and exhaust system 

was hot. Regardless of how well the filter worked and reduced DPM emissions, all the 

mechanics wanted to know was when the system would be removed. 

Management had a completely negative perception of this system primarily because of 

high operational and maintenance costs, poor reliability and questionable performance. 

The major costs were associated with developing and maintaining infrastructure for the 

bulk fuel blending. High costs made this system completely unacceptable from the 

management perspective. The high filtration efficiencies observed during the tests while 

the filters were not compromised were very encouraging for management and had they 

continued reliably without failures, the perception may have been quite different. 

Oberland Mangold Octel DPF System Installed on VH181

Truck

Out of the four systems tested in the project, the Oberland Mangold DPF was the only 

one manufactured outside of North America. Manufactured in Germany, the system was 

used mostly in lighter duty applications but also on a few production units at an 

underground mine in Germany. In the specifications for the project, DPF manufacturers 

were asked to keep DPF dimensions within the size limits of the exhaust components that 

existed on the test vehicles. For the truck applications this was a significant challenge 

because of the size of the large engine and relatively small space in the engine 

compartment available for exhaust components. The first version of Oberland Mangold’s 

DPF was manufactured to meet these size restrictions. However, as backpressure was a 

problem right from the installation, it became quickly apparent that the filter was 

undersized for the application. The manufacturer requested the opportunity to design and 

construct a second version of the system. The original DPF, which contained 25 glass 

fiber cartridges, was replaced with a new DPF with 52 glass fiber cartridges. The original 

DPF was installed in June of 2000. The replacement unit was installed two months later 

in August of 2000. 

The significantly larger second version of the DPF brought quick resolution to the 

problem of backpressure. This oversized DPF system with the glass fiber filter media had 

the least problems with backpressure of all four tested systems. However, the increase in 

physical dimensions created problems for the mechanical department. The mechanics 

encountered difficulties servicing the engine around the DPF. This DPF system exhibited 

somewhat lower filtration efficiency the other tested systems. 

Chronology of Events 

 June 2000 – The system was installed on VH181 that had 2265 operating hours 

since new 

 June 2000 – The first efficiency measurements performed with original version of 

DPF in place 
- 62 - 

 August 2000 – The second version of DPF system replaced the original one that 

accumulated 335 hours. 

 February 2001 – Isolated zone testing and the second efficiency evaluation 

 June 2001 – The third efficiency evaluation 

 November 2001 – The final efficiency evaluation 

 February 2002 – De-commissioned of the system at Brunswick Mine

o The 2nd DPFsystem accumulated 2900 operating hours and vehicle 

used 21,800 gallons of fuel – 

o 32% of total hours the vehicle was operated at idle 

 September 2002 – The system was bench tested at CANMET, Bells Corners 

laboratory 

Exhaust Temperature and Backpressure 

The data that was retrieved from the datalogger was backed up by measurements of 

backpressure performed by mine mechanics at monthly intervals. The backpressure 

reached a plateau of approximately 120 mbar or 50 inches of water. The data presented in 

Figure 35 shows backpressure values increasing and decreasing in a regular pattern, 

which indicates at least partial regeneration occurring during the duty cycle. The exhaust 

temperature traces show temperatures at the inlet to the system well above 400° C. The 

temperature profile compares well to one for the other truck used in the project but the 

backpressures and apparent regeneration profiles are drastically different. The glass fiber 

filter media appear to have captured less particulate than silicon carbide monolith media 

used in the other system. The lower loading inside the filter media made it easier to 

regenerate when temperatures reached high enough levels to ignite the trapped soot. 

Figure 35 - Oberland Mangold Exhaust Temperature and Backpressure
- 63 - 

Gaseous Emissions 

The results of gaseous emissions measurements made on VH181 truck equipped with the 

Oberland Mangold DPF system are shown in Figure 36. The non-catalyzed DPF with 

glass fiber media did not affect either carbon monoxide or nitrogen dioxide emissions. 

Carbon dioxide emissions and exhaust temperatures were consistent throughout the tests 

with the exception of the final test indicating that proper testing protocol was followed 

with full engine stall.

Figure 36 – Gaseous Emissions For VH181 With Oberland Mangold DPF 
- 64 - 

Diesel Particulate Matter (DPM) Emissions 

The results of particulate matter emissions measurements, shown in Figure 37, indicate 

that fiber knitted filter consistently exhibited lower filtration efficiency than the other 

three wall flow monolith DPF systems tested in this study. The first set of results was 

generated in June 2000 during the tests involving the original DPF with 25 filter 

cartridges. The other three tests were performed with the larger, 52 cartridge DPF system. 

The efficiency of the system was found to be lowest when particulate matter emissions 

obtained for tests at mode 4 (idle) were used for calculation. The PM emissions 

measurements obtained for remaining modes were providing consistent results and 

showed as low as 90% or slightly below. The NIOSH 5040 method analyses agreed very 

closely with NanoMet results in the 2nd and 3rd sets of tests but were 5 to 10% below 

NanoMet results in the 1st and 4th sets. 

Figure 37 – DPM Filtration Efficiencies For Oberland Mangold DPF System on VH181 Truck
- 65 - 

The results of Bacharach smoke index (BSI) tests shown in Figure 38 agree better with 

the NIOSH 5040 method results than with the NanoMet results. Whereas the BSIs 

observed for the other three tested DPF systems that are using wallflow monolith 

technologies were consistently between 0 or 1 at the outlet, the BSIs for Oberland 

Mangold System that utilize fiber cartridges were closer to 4 or 5 on 0 to 9 scale. 

Bacharach testing results were consistent throughout the project. 

Figure 38 - Oberland Mangold Octel Bacharach Smoke Density Results

Observations 

Mechanics who worked on the vehicle and engine maintenance complained about 

physical size of the DPF system. It was a challenge to perform maintenance especially 

when the engine had been running and the exhaust system was still hot. They also pointed 

to the absence of a mechanical coupling on the DPF housing needed to facilitate 

inspection and periodic cleaning of the system. 

Operators were indifferent to the performance of the DPF system. This was less due to 

performance of the system but more to the fact that the truck was operated in main 

haulage drifts where high quantities of flow through ventilation air were available. 

Additional heat created by the DPF was not noticed to be a problem. 

Relatively low filtration efficiency, the burden of maintaining the fuel supply 

infrastructure and relatively high costs associated with supplying the vehicle with bulkblended fuel were recognized by management to be the major deficiencies of the system. 

The relatively successful passive regeneration process and total volume of the unit were 

reasons that engine backpressure stayed near or below maximum limits prescribed by 

engine manufacturer. The maintenance requirements for this system were relatively low. 
- 66 - 

The extent of the requirement for supplying vehicles with fuel doped with additive was 

found to be ultimately the deciding factor against the acceptance of this DPF system by 

mine management. 

IISSOOOLLLAAATTTEEEDDD ZZOOONNNEEE SSTTTUUUDDDYYY

Objective and Scope

One of the objectives of the project was to assess the effectiveness of the DPF systems 

technology on concentrations of DPM and gases in mine air and on exposure of vehicle 

operators. In order to accomplish this it was necessary to design a controlled study in a 

section of the mine that did not contain confounding diesel exhaust contaminants from 

equipment not outfitted with DPF systems. This required isolating an operating zone with 

well-defined and controlled fresh air ventilation with no losses, and eliminating 

interference sources from other diesel powered vehicles. 

Experiment Methodology

The zone at the 525-5 sub level of Brunswick Mine was found to meet criteria for 

conducting this study. The Brunswick management team provided an entire operating 

level in the mine, where production activity had ceased, but ground control and 

ventilation were maintained. A 400-meter section of drift on 525-5 sub level was 

completely isolated from the other parts of the mine by installing two bulkheads. The 

zone was ventilated with fresh, DPM-free air from the intake fan system. The layout of 

525-5 sub level is shown in Figure 39 with the V3 intake raise at one end and the exhaust 

raise at the opposite end of the zone. 

Each of the vehicles tested in this study was operated inside the 400-meter zone while 

repeating a simulated production cycle. The vehicles were operated with the bucket or 

box filled with ore. The cycle, developed exclusively for this study, simulated duty cycles 

observed for LHD vehicles in normal operation at the mine. The cycle consisted of the 

following operations: (1) In the loading cycle simulation at the air intake side of the zone 

the vehicle was parked for a period of 2 minutes and operated over two steady-state 

operating conditions. For 15 seconds the engine was run at full throttle with torque 

converter and hydraulics stalled. This was followed by a 15 second period at full throttle 

with transmission in neutral and no load on engine. These two conditions were repeated 

four times each in a two minute period. This simulated the mucking cycle without 

producing dust normally associated with mucking process. (2) The vehicle then trammed 

for 400 meters along the drift to the exhaust end of the zone where the vehicle was turned 

around and parked to simulate the dump portion of the cycle; (3) The dump cycle 

simulation was simply a steady state 30-second run at full throttle with transmission in 

neutral and no load on engine; (4) After finishing with the dump cycle the vehicle then 

returned to the fresh air intake end of the zone to repeat the full cycle. Each vehicle was 

operated for a period of 4 hours repeating the described 8-minute cycle. A single 

experienced operator operated all tested vehicles in similar fashion. 
- 67 - 

The ventilation flow rate through the zone was maintained at approximately 849.5 

m3/min (30,000 cfm), This exceeded the CSA certified ventilation rate for the tested 

vehicles of 623 m3/min (22,000 cfm) for LHDs and 774.7 m3/min (26,300 cfm) for trucks 

[Natural Resources Canada, 2003]. It was below the standard ventilation rate used for the 

tested vehicles at Brunswick Mine of 975.5 m3/min (34,450 cfm) for LHDs and 1125.5 

m3/min (39,750 cfm) for trucks [New Brunswick, 1996]. 

Figure 39 - 525-5 Sublevel Isolated Zone

DPM sampling stations were established inside the zone at the following locations: (1) at 

the air intake side of the zone, (2) on the vehicles near the operator’s compartment, and 

(3) at the exhaust side of the zone. At the exhaust side station the instrumentation was set 

to measure size distribution and number concentration of particles. 

All ventilation and vehicle operation parameters relevant for the study were closely 

monitored and controlled. 

In order to assess the potential of the filter systems to improve air quality in the mine 

over current existing conditions, emissions from the four vehicles equipped with DPFs 

were compared with emissions from two vehicles equipped with diesel oxidation catalyst 

(DOC) and muffler as mandated by existing New Brunswick provincial regulations [New 

Brunswick, 1996]. At Brunswick Mine all LHDs and trucks were commissioned with 

identical specifications and configurations. Engine, power train, hydraulic, frame and all 

other vehicle systems were identical across the ST8-B LHD fleet and the MT436-B truck 

fleet. All vehicles tested in the isolated zone study had accumulated relatively low total 

operating hours prior to the testing. The four vehicles equipped with the DPFs had 

accumulated between1200 and 2200 total operating hours since delivery from the vehicle 
- 68 - 

manufacturer. The LHD and truck equipped with DOCs were almost brand new with only 

500 and 200 operating hours, respectively. 

The six vehicle and DPF or DOC combinations tested in the study were: 

1. LHD ST8-B, VL244 equipped with ECS CatTrap DPF system; 

2. LHD ST8-B, VL247 equipped with DCL BlueSky DPF system; 

3. LHD ST8-B, VL254 equipped with diesel oxidation catalyst and muffler; 

4. Truck MT436, VH183 equipped with ECS Octel DPF system; 

5. Truck MT436, VH181 equipped with Oberland Mangold DPF system; 

6. Truck MT436, VH188 equipped with diesel oxidation catalyst and muffler. 

 

Measurement of Ambient Concentrations of DPM

A total of seven samples were collected at each of the three sampling stations inside the 

isolated zone. Five of the samples were analyzed for carbon content using NIOSH 

Analytical Method 5040 [NIOSH Manual for Analytical Methods, 1999]. The other two 

samples were analyzed for respirable combustible dust (RCD) [Grenier et al. 1996]. The 

trains for carbon analysis consisted of a pre-separator 10mm York nylon cyclone, 37-mm 

cassette with quartz fiber filter, tubing, and sampling pump calibrated at 1.7 L/min. At the 

fresh air intake and exhaust sampling stations the samplers were positioned on a 2 by 4 

meter screen to compensate for potential spatial variation of the concentrations across the 

drift. The samplers on the vehicle were placed in a basket mounted on top of the engine 

compartment directly in front of and within one meter of the operator. CANMET’s 

Sudbury U/G Mine Environment Team conducted all DPM sampling and analysis. 

In addition, extensive ambient measurements of particulate matter concentrations were 

taken at the exhaust sampling station. Because of the structured vehicle cycles and the 

controlled ventilation rate inside the zone, the concentration of airborne diesel particulate 

matter at the most downstream end of the zone were the heaviest with the most uniform 

spatial and temporal distribution. 

A team from the NIOSH Pittsburgh laboratories used the Scanning Mobility Particle 

Sizer (SMPS) to measure size distribution and number concentrations of airborne 

particles at the sampling station located at the most downstream end of the zone. The 

SMPS instrument was used for direct measurement of ambient concentrations of particles 

with electrical mobility diameter ranging from 10 – 392 nm. The measurements were 

performed at three points during each repetition of the duty cycle: (1) while the vehicle 

was performing a simulated load cycle at the most upstream section of the zone, (2) while 

the vehicle was tramming from load to dump location, and (3) while the vehicle was 

performing a simulated dump cycle at the downstream section of the zone. The quasi 

steady-state measurements were performed using 90-second scans. The results shown in 

Figure 42 are based on integral count concentrations for each vehicle and the sampling 

averaged over number of measurements performed during the four-hour test period. 

A total of 15 DPM samples for carbon analysis were gathered for each of the tested 

vehicles. Five samples were collected at each of the following stations: (1) the fresh air 

intake, (2) the vehicle operator, and (3) the exhaust sampling station. The DPM samples 
- 69 - 

were analyzed for total carbon (TC) by CANMET’s Laboratory using NIOSH Analytical 

Method 5040 [NIOSH Manual for Analytical Methods, 1999]. The analysis showed that 

the fresh air inlet to the zone had very low concentrations of TC. The analysis also 

showed that the TC concentrations were slightly higher at the exhaust sampling station 

than at the vehicle operator. 

Results 

The results of analysis of the five samples collected at the exhaust sampling station are 

presented in Figure 40 and Figure 41. The results are presented as average concentrations 

for the 5 samples analyzed per vehicle. In order to illustrate the potential of the DPF 

systems to reduce DPM concentrations in mine air the results are presented as 

concentrations of total and elemental carbon respectively in Figures 40 and 41. The 

results are compared against the proposed regulations and limits from MSHA [MSHA, 

2001] and ACGIH [ACGIH, 2001] at the time of the study which became the targets to 

attempt to achieve with the DPF technology during the project. There are some provinces 

in Canada which adopt the ACGIH accepted limits on DPM. Since the time the study was 

conducted both MSHA and ACGIH have made changes to these regulations and 

proposed limits. 

Figure 40 – Total Carbon Concentrations in Isolated Zone for Different Test Vehicles 
- 70 - 

Figure 41 - Elemental Carbon Concentrations in Isolated Zone for Different Test Vehicles

Both LHDs retrofitted with DPFs emitted significantly less TC and EC than the LHD 

equipped with a DOC, although the observed concentrations at the exhaust station were 

slightly higher than proposed ACGIH limits of 0.05 mg/m3 of TC or 0.02 mg/m3 of EC. 

The differences in concentrations of TC and EC emitted by the trucks equipped with 

DPFs and the truck equipped with a DOC were somewhat less pronounced. The ambient 

concentrations of TC measured when VH183 with the ECS Octel DPF system was 

operated in the zone were much higher than expected. VH181 with the Oberland 

Mangold DPF exhibited much lower EC emissions than the baseline truck, VH188. 

In interpreting these results it is also seen as important to take the following into account: 

1. The zone was ventilated at or below 106 cfm/bhp, the rate mandated by the 

provincial government [New Brunswick, 1996] 

2. Time averaged concentrations obtained on the exhaust sampling station should be 

higher than those measured at the operator. The operator samplers moved 

continuously back and forth between fresh air and the exhaust station whereas the 

exhaust station samplers were continuously exposed to maximum particulate 

loading inside the zone. Therefore, obtained values obtained where air was 

exhausted should represent the worst-case scenario. 

3. All four vehicles equipped with DPFs showed visible signs of exhaust leaks 

between the exhaust manifold and the filter. It was not possible to quantify these 

leaks, but our assumption is that they contributed significantly to the concentration 

of DPM in the mine air. The ambient concentration samples did not provide 
- 71 - 

enough data to distinguish results between DPFs with leaks but the SMPS data 

results did show that VL247 with the DCL Bluesky DPF which had the largest and 

most visible leaks, had a distinguishing difference from the others with respect to 

particle size and number. 

A scanning mobility particle sizer was used to measure size distributions of the particles 

in mine air at the downstream end of the zone. The measurements were performed for all 

tested vehicles three times during each of the 8-minute load-haul-dump cycles. During 

the four-hour test period, more than thirty sets of data were collected per vehicle. The 

obtained concentrations were corrected for fluctuations in the ventilation rate that 

occurred between the tests. The repeatability of measurements, observed for all vehicles, 

indicated stability of test parameters influencing distributions, such as ventilation rates, 

duty cycle, ambient conditions, etc. 

The measurements showed that size distributions of particles emitted by vehicles 

retrofitted with DPFs are bimodal with relatively high concentrations of nanoparticles 

(below 50 nm). The emissions from vehicles equipped with DOCs were characterized 

with relatively high concentrations of particles below the 100 nm size range. 

Figure 42 - Particle Concentrations by Number Measured in Isolated Zone for Different Test 

Vehicles 
- 72 - 

Figure 43 - Particle Concentrations by Volume Measured in Isolated Zone for Different Test Vehicles

All filtration systems except the DCL Bluesky filter installed on VL247 demonstrated 

high efficiency in reducing the number of particles emitted. (See figures 42 and 43.) For 

the DCL Bluesky system, the concentrations of particles by number were even higher 

than for the LHD equipped only with the DOC. Neither the DCL Bluesky system nor the 

ECS Octel system offered expected reductions in particle volume. The relatively low 

efficiency of the DCL Bluesky system was attributed to sizeable exhaust leaks between 

the turbocharger and filter. The results showing poor performance of the ECS Octel 

system are in good agreement with the results of carbon analysis. 

ISOLATED ZONE STUDY CONCLUSIONS

The isolated zone study showed that significant reductions in concentrations of diesel 

particulate matter in underground mines are achievable with diesel particulate filter 

technology. The study also demonstrated several measurement and analysis methods 

available to the underground mining industry for evaluating performance of filter 

technology. 
- 73 - 

Extensive measurements showed that three out of four tested filters offered excellent 

reductions in DPM concentrations. All DPF systems with the exception of the ECS Octel 

filter performed with high filtration efficiencies. The ECS Octel measurements indicated 

premature failure of the filter. The post-test investigation revealed that the filter media 

had been cracked internally. Traces of black soot were seen at the outlet face of the filter. 

The premature failure was attributed to uncontrolled regeneration as described earlier in 

the report. 

The comparison of the results of SMPS and tailpipe measurements revealed important 

issues with the complex filter efficiency evaluation process. The SMPS measurements in 

mine air indicated high ambient concentrations of particles emitted by a system which 

had shown high filtration efficiencies according to tailpipe emissions measurements. This 

alarming discrepancy in the tailpipe emission measurements and ambient concentrations 

of particles was explained by sizeable leaks discovered in the exhaust system between the 

engine and the DPF. Introducing a DPF into the exhaust system can significantly increase 

engine exhaust backpressure, resulting in leaks and increased ambient emissions. These 

fugitive emissions are unlikely to be caught with tailpipe measurements alone. This 

emphasizes the importance of maintaining integrity of the exhaust system upstream of the 

filter, as well as the importance of ambient exposure monitoring. 

The measurement methods employed in the isolated zone study provided consistent and 

valuable data necessary for better understanding of processes governing the formation 

and transformation of diesel particulate matter in mine air. The study demonstrated 

several methods available to the underground mining industry for assessing the efficiency 

of DPF systems. The methods demonstrated different levels of complexity and accuracy. 

The tailpipe measurement instruments were able to measure the 99% efficiency quite 

accurately but only the ambient measurements were able to detect the effects of the leaks. 

The principal conclusions to be drawn from the testing done inside the isolated zone 

are: 

1. Diesel particulate filter technologies were demonstrated to be very efficient in 

reducing DPM concentrations. At a ventilation rate appropriate for the engine, the 

ambient DPM concentrations achieved during this study are well below the MSHA 

regulatory limits at the time of the study [MSHA, 2001] and almost meet ACGIH 

recommended diesel particulate exposure limits proposed at the time of the study. 

[ACGIH, 2001] 

2. The ability to attain and sustain diesel equipment within these limits would depend 

on the ability of mine maintenance personnel to measure performance and 

maintain the systems accordingly. 

3. Filter efficiency must be evaluated using both tailpipe and ambient measurements. 

These two types of measurement complement each other. 

4. The importance of maintenance cannot be overemphasized – undetected failures 

and leaks in the DPF system can potentially result in particulate exposure levels 

that can be higher than current levels. 
- 74 - 

 

LLAABBBOOORRRAAATTTOOORRRYYY EEVVVAAALLLUUUAAATTTIIIOOONN OOOFFF DDPPFF SSYYYSSSTTTEEEMMMSSS

Laboratory Bench Testing

Following the field de-commissioning, the four DPF systems tested at Brunswick Mine 

were sent to the CANMET diesel testing laboratories in Bells Corners, Ontario. The 

objectives were to establish efficiency of the systems using laboratory data and validate 

data obtained during in-mine evaluations. The CANMET-MMSL diesel laboratory is ISO 

9001:2000 certified. An evaluation method for testing the DPF systems was established 

based on the ISO 8178 test protocol. The laboratory and test parameters are given in 

Table 12. The DPF systems were mounted on a Detroit Diesel Series 60 engine identical 

to those used in Brunswick LHDs. The PAS 2000 PAH monitor, the same instrument 

used in the field evaluations was used for efficiency measurements. Emissions DPM, 

hydrocarbons, CO, NO, and NO2 were measured using laboratory grade analytical 

instrumentation.

The ECS Octel system had been burnt out by uncontrolled regeneration during the field 

study, and could not be tested. The three remaining systems included in the evaluation 

were the ECS CatTrap, DCL Bluesky, and Oberland Mangold Octel system. Before 

testing the three DPF systems, a baseline set of data was collected on the test engine. 

Table 12 - Laboratory Bench Test Parameters and Protocol

TEST ENGINE SPECIFICATIONS

Manufacturer and Model Detroit Diesel Series 60 

Displacement 11.1 liter 

Power Rating @ 2100 rpm 325 HP – 242 kW 

TEST FUEL SPECIFICATIONS

Code CGSB-3.16 

Classification Mining Diesel Fuel 

Sulphur Content 275 PPM 

Additives Octimax 4804 (Oberland Mangold only) 

ANALYTICAL INSTRUMENTATION

Elemental Carbon (DPM) NanoMet Mini Diluter with EcoChem PAS 2000 

Total DPM Sierra Instruments BG-2 Micro Dilution with Gravimetric 

Analysis 

Total Hydrocarbons (THC) heated flame ionization detector (HFID) 

Carbon Monoxide (CO) non-dispersive infrared (NDIR) 

Nitric Oxide (NO) heated chemiluminescent detectors (HCLD) 

Oxides of Nitrogen (NOx) heated chemiluminescent detectors (HCLD) 

Nitrogen Dioxide (NO2) calculated = NOx - NO2

TEST PROTOCOL – MINE TEST CYCLE

FTC Full Torque Converter Stall – 1950 RPM 
- 75 - 

FH Full Converter and Hydraulic Stall – 1650 RPM 

HI Rated Hi Idle No Load – 2100 RPM 

LI Low Idle No Load – 600 RPM 

SF Snap Acceleration Free No Load – 3X 

SS Snap Acceleration Torque Converter Stall – 3X 

TEST PROTOCOL – ISO-8178, 4 MODES

Mode 1 Rated Speed 2100 RPM @ 100% Load 

Mode 3 Rated Speed 2100 RPM @ 50% Load 

Mode 5 Intermediate Speed 1260 RPM @ 100% Load 

Mode 7 Intermediate Speed 1260 RPM @ 50% Load 

 

BENCH TEST RESULTS

The testing performed on simulated mine test cycles correlated well to the in-mine 

efficiency tests. Filtration efficiency was found to be 80 to 91% for the ECS CatTrap 

system, 91 to 96% for the DCL Bluesky, and 74 to 92% for the Oberland Mangold Octel 

system. 

The PAS 2000 results that are shown in Figures 44, 45 and 46 illustrate the elemental 

carbon reductions during snap acceleration test modes in comparison to the baseline 

emissions. The DCL Bluesky consistently exhibited better efficiency than both the ECS 

CatTrap and Oberland Mangold Octel systems. 

Figure 44 – Results of Measurement with PAS 2000, Mine Test Cycles 
- 76 - 

Figure 45 – Results of Measurement with PAS 2000, Snap Acceleration No-Load Tests 

Figure 46 – Results of Measurement with PAS 2000, Snap Acceleration under Load Tests 

The testing performed over four ISO-8178 modes provided additional insight in 

performance of the DPF systems. During these tests laboratory grade instrumentation and 

methods were used to measure emissions of DPM, hydrocarbons, carbon monoxide, nitric 

oxide, and nitrogen dioxide. The results of total DPM emissions measurements shown in 

Figure 47, demonstrated significant reductions in DPM emissions when the DPF systems 

were tested. The exception was the DCL Bluesky system. When this system was tested 
- 77 - 

over mode 5 relatively high DPM emissions were recorded. This was most likely caused 

by the platinum catalyst washcoat employed with the DCL system, which depending on 

catalyst formulation and potency and exhaust temperatures tend to increase sulphate 

formation and therefore increase total DPM emissions. While the sensitivity of sulphate 

creation to exhaust temperature is quite evident in mode 5, there is no way of making this 

determination with absolute certainty. This finding is significant because until the postfield bench tests, all results for DPM and filtration efficiency indicated that the DCL 

Bluesky had a slightly higher efficiency than the other systems. The concentrations of 

carbon monoxide for all four test conditions were found to be fairly unaffected by DPF 

systems with the exception of the DCL Bluesky system. This system greatly reduced CO 

concentrations. These reductions can be attributed to the activity of the platinum catalyst 

used in the DCL system.. Similarly, the hydrocarbon emissions measurements shown in 

figure 49 indicate a larger reduction in HC emissions in the case of the DCL system again 

due to the activity of the platinum catalyst. The other systems also reduced hydrocarbon 

emissions but not to the extent observed with the DCL system. The platinum catalyst in 

the DCL system also increased conversion of NO to NO2 as seen in Figure 50. The 

concentrations of NO2 downstream of the Oberland Mangold Octel system were much 

lower than concentrations established during baseline and ECS CatTrap tests. 

Figure 47 – Average Total DPM Emissions Over Four-Mode Tests
- 78 - 

Figure 48 – Average Carbon Monoxide Emissions Measured Over Four-Mode Tests

Figure 49 – Average Hydrocarbon Emissions Measured Over Four-Mode Tests
- 79 - 

Figure 50 – Average Nitrogen Dioxide Emissions Measured Across Four-Mode Tests

Post Study Inspections

The final stage of evaluation of the DPF systems was intended to be a full destructive 

testing and autopsy to be conducted by the DPF manufacturers. The plan was to send the 

systems to manufacturers upon return of the systems from bench testing. In some cases 

this was accomplished and in other cases DPFs were reinstalled on the vehicles for 

continuation of in-field evaluation or taken for independent testing by third party. 

Regardless of inspection techniques post study inspections revealed interesting 

performance related information for each DPF. 

ECS CatTrap 

Inspection and non-destructive testing on the ECS CatTrap was performed twice during 

the study. The first inspection was after the DPF system accumulated 1000 operating 

hours and was removed from the vehicle and sent back to the manufacturer for cleaning 

and inspection. The second was done after laboratory testing. At that time the DPF had 

accumulated 3000 operating hours since cleaning and inspection. Inspection was made 

with a video boroscope and visual inspection as well as measurement of mass 

accumulation of ash inside the filters. The inspection revealed that ash had built up inside 

the filter between 6 to 7 inches deep from the outlet face back towards the inlet as shown 

in Figure 51. An area of melting and pitting was evidenced close to the outlet face of the 
- 80 - 

top filter in the DPF. In light of these findings the manufacturer ECS recommended a 

cleaning frequency of 1000 hours. Frequent cleaning should minimize the buildup of 

accumulated ash. Since cleaning with compressed air alone was insufficient ECS 

recommended cleaning in a kiln where the filter element can be heated while ash is 

removed by compressed air. 

Figure 51 - Non-Destructive Testing of ECS CatTrap 

DCL Bluesky 

The DCL Bluesky system remained at the CANMET laboratories after the bench testing 

to undergo further independent testing at the request of the manufacturer. A thorough 

visual inspection was made at the laboratory. The boroscope was not available for 

detailed internal inspection of the filter. Determinations were made based only on visual 

observations of the system. The silicon carbide filter monolith showed no signs of 

mechanical fatigue or failure. There was no evidence of any bypassing or deterioration of 

the matt seal between the monolith and inside diameter of the DPF housing. 

Discoloration of the silicon carbide monolith at the outlet face was believed to have been 

caused by accumulations of water inside the outlet plenum of the DPF. The most likely 

reason for this is steam cleaning at preventive maintenance intervals at the mine. Water 

directed into the tailpipe of the exhaust would flow towards the DPF where there was a 

drop from the 5” pipe to the cone of the outlet plenum and where water could settle. This 

would build up until the engine was operated at full load for an extended period and the 

water could be blown back out naturally. Despite evidence of several modifications 

during the 4000 hour installation to the mounting of the electric heater element and the 

butterfly valve at the filter inlet, the DPF appeared to be mechanically sound with some 

oxidation evident at the housing flanges. 
- 81 - 

Figure 52 - Inlet and Outlet Faces of DCL Bluesky DPF

ECS Octel 

The filter monoliths in the ECS Octel DPF system failed twice over the duration of the 

project. The first set failed at 2500 hours of operation and the second set failed with 1500 

hours of operation. A detailed evaluation and autopsy on the first set of failed filters was 

performed by the manufacturer, ECS. The second set of failed filters was not evaluated so 

the boroscope results herein are from the first set. The results showed that both filters 

were badly cracked across the entire outlet face from 1” to 2” in depth. In addition, both 

filters were badly plugged with soot through almost the entire volume with a few more 

cracks towards the center of the filter bodies as well. The failure of the second set of 

filters had obvious visible cracks and separation of the cubic silicon carbide segments 

that formed the monoliths. The first assessment of this condition was that vertical stress 

and mechanical shock due to the vertical mount of the twin filters had caused the cubic 

segments to shear at the cemented joints. Final evaluation by ECS attributed the cause of 

the failure to lack of heat treatment during the assembly stage of the filter. A combination 

of receiving green silicon carbide monoliths and the treatment for mat retention was 

insufficient to calcinate the cement with the segments. The failed silicon carbide 

monolith is shown in Figure 53 with plugged inlet and cracked outlet faces. 
- 82 - 

Figure 53 - Inlet and Outlet Faces of ECS Octel DPF

Oberland Mangold Octel 

The Oberland Mangold DPF was the only system to have full destructive testing and 

inspection conducted. The DPF was constructed such that the housing was welded as a 

continuous shell from inlet to outlet with no mechanical flanges other than the 5” inlet 

and outlet connections. This meant firstly, that there was no allowance made in the design 

for periodic disassembly and cleaning of the filter. Secondly, this meant that dismantling 

of the filter could only be done by cutting the assembly into sections starting with the 

outside shell and working inwards. The 52 glass fiber cartridges were welded onto a solid 

manifold plate that was in turn welded inside the filter housing. Mechanically, this 

created a rugged and durable design which appeared to withstand the challenges of the 

operating environment. On first observation, the glass fiber cartridges showed very little 

sign of mechanical deterioration or material failure, despite 3000 hours of operation. On 

further inspection, however, high heat loading and discoloration were evident in a 

circular area in the center of the manifold plate, indicating uneven temperature 

distribution. 

The cartridges were cut off close to the manifold plate to inspect the internal or inlet face 

of the filter cartridges. This revealed a large accumulation of iron oxide from the Octimax 

4804 additive (see Figure 54). The filter had trapped the oxidized additive components. 

This indicated a need for a mechanical design which would accommodate periodic 

cleaning of the filter, and perhaps more importantly, the need to maintain the mechanical 

integrity of the entire exhaust system and minimize leaks from which additive particles 

could escape. 
- 83 - 

Figure 54 - Oberland Mangold Fiber Cartridges and Iron Oxide Accumulation 

CCOOONNCCCLLUUUSSSIIIOONN

This research project was undertaken to test the effectiveness of diesel particulate filters 

in reducing diesel emissions and exposures in an underground mining environment. The 

work was complex and required a number of sub-studies. 

The project first established a process for choosing appropriate DPF systems for specific 

mobile equipment applications. This involved measuring and logging vehicle duty cycles, 

providing this information in a request for proposals from DPF manufacturers, and 

evaluating proposals. The RFP document can be used as a template for future selection 

processes and is included as an appendix to this report. 

Four DPF systems were retrofitted on mine vehicles, and tested in a long-term field 

study, to investigate their effectiveness, durability, maintainability, and costs. This 

research was quite complex, because each system introduced important variables 

including: 

 size and configuration of the DPF, ease of installation and later access to the vehicle 

engine for maintenance; 

 ease of disassembly, inspection and cleaning; 

 duty cycle and exhaust temperatures of the vehicle on which the DPF was mounted; 

 variables related to regeneration systems, including use of fuel additives in some 

systems, and catalyst materials used to lower the temperature for passive regeneration 

in some systems, affecting gaseous as well as particulate emissions; 

 use of active regeneration components such as internal or external heaters; 
- 84 - 

 a need for vehicle operators to develop new habits and practices to keep the DPF 

systems regenerating on a regular basis and the engines operating within tighter 

performance standards . 

 a need for maintenance mechanics to understand the DPF system technologies and 

maintain them along with related vehicle systems (engines) to high performance 

standards with proper verification and diagnostics. 

This study has reported extensively on the impact of these variables, since they are 

important issues for any effort to utilize DPF systems underground. The lessons of this 

experience are: 

1. Choose vehicles and applications by a prioritized list that includes factors such as 

engine duty cycle for regeneration, potential impact to reducing worker exposure 

to DPM, operability and maintainability, and retrofit requirements. 

2. Use basic off-the-shelf portable temperature sensor and logger technology to 

acquire exhaust temperature profiles for prospective vehicles for a sufficient 

period to cover the full spectrum of operating and production modes repeatedly. 

3. Include mine management, production and maintenance personnel as well as 

vehicle and DPF manufacturers to engineer each individual installation from 

selection through installation and verification. 

4. Begin communication and education programs with the production and 

maintenance departments before the DPF systems are chosen and implemented. 

Build and sustain the education program as a continuous process rather than a one 

time course. 

5. Have vehicle and DPF manufacturers supply retrofit applications as a complete 

kit that includes all necessary hardware including frame modifications. 

Modification kits need to be agreed upon by mine operations and maintenance 

departments, engine, and vehicle manufacturers before being confirmed for 

installation. The kit should come with parts and service manuals that cover not 

only the DPF system but all of the associated hardware for the retrofit. 

6. Make use of existing on-board monitoring, diagnostics and protection systems 

such as electronic engine controls and ECMs. Make sure a monitoring system is 

in place for the operator with dashboard display and protection for exhaust 

backpressure. This system should be as simple and maintainable as possible. 

7. Ensure that regeneration assistance technologies whether passive wash coat 

catalysts, fuel borne catalysts or active heater systems are well understood by 

operators and mechanics and closely monitored. Issues such as NO2 conversion 

by platinum catalysts for example, need to be monitored monthly at a minimum 

and strict limits adhered to. 

8. The installed DPF systems should be managed by the maintenance planning 

department as a major component as is done with engines, transmissions, axles, 

etc. This way component history, hours and change out and cleaning schedule can 

be effectively managed. 

The performance of the four DPF systems each brought their own lessons and knowledge 

gained regardless of how successfully it performed and stood the test of time. 
- 85 - 

The ECS CatTrap performed well consistently through more than 4000 hours of 

operation in the project. The twin ceramic monolith filters with base metal catalyst wash 

coat supported full passive regeneration with no conversion of either CO or NO2. The 

filtration efficiency testing that was done a three intervals during the project showed 

better than 99% reduction in DPM from inlet to outlet sided of the filter when new and 

still above 95% efficient with 4000 operating hours. Tests done at the laboratory post 

field test showed 80-91% reduction efficiency based on similar engine, test cycles and 

analytical instrumentation. Non destructive testing done post field test revealed some ash 

buildup 6 to 7 inches in depth from the outlet face of the filter and some slight melting 

and pitting in one of the filter monoliths. Following these tests the CatTrap system was 

returned to Brunswick Mine and re-installed on another ST8B LHD vehicle. 

The DCL Bluesky system performed very well in terms of filtration efficiency but 

demonstrated problems with NO2 conversion due to the platinum catalyst. Problems with 

the active electric regeneration system followed the system from start to finish of the 

project. Initial design problems were rectified quickly but acceptance of the requirement 

for plugging in each shift was always poor. Four sets of performance tests done across 

4300 hours of operation showed consistent filtration efficiencies at 99%. Testing of 

gaseous emissions during the field tests showed between two to four fold increases in 

NO2 from filter inlet to outlet. Tests done at the laboratory were consistent with the field 

tests for gaseous emissions and CO and NO2 in particular. The laboratory tests did reveal 

however a sharp increase in total DPM measured at ISO 8178 mode 5 that was not seen 

with the PAS 2000 instrument testing for elemental carbon. This was attributed to the 

creation of sulphate by the platinum catalyst wash coat on the filter. Mechanical 

durability of the system was very good other than the failed heater elements in the twenty 

months of field operation. The silicon carbide filter monolith remained structurally intact 

with no bypass or failure of the mat seal between filter and housing. 

The ECS Octel system was the most disappointing of the four systems in terms of 

performance and reliability. Insufficient regeneration throughout the field study led to the 

eventual failures of two sets of filters. The emissions tests tracked these failures well and 

the mechanics were able to closely monitor exhaust back pressure to protect the engine 

despite the failure of the DPF system. A combination of component design, DPF sizing, 

and below expected performance of the Octel fuel borne catalyst contributed to the 

failure of the system. The laboratory tests and inspection at the conclusion of the project 

were not performed with the DPF system as the set of filters had been compromised in 

the last months of the field test. 

The Oberland Mangold Octel system was reliable throughout the project though filtration 

efficiencies consistently measured less than the other three systems. This was due to the 

difference in applying fiber cartridge filter media instead of wall flow monoliths. 

Filtration efficiency was measured closer to the 90% range as compared to 98% and 

higher with the wallflow monolith systems. The up side of this however was that exhaust 

back pressure was much lower than the other systems especially the other MT 436 truck. 

This was attributed to the difference in filter media in combination with the over sized 
- 86 - 

filter volume. The laboratory test results correlated well to those from the field tests. The 

inspection of the DPF system following laboratory testing revealed very good structural 

integrity of the system after 3000 hours of operation but a large buildup of iron oxide on 

the inlet side of the filter cartridges. This buildup was sourced from the Octel fuel 

additive which contained the iron and strontium compounds. The amount of buildup 

highlighted the need for a system design that could accommodate disassembly and 

cleaning at regular intervals. 

As with any project at a mining operation, this project had a finite life and thus the 

acceptance by management, production and maintenance staff reflected that. Projects and 

processes are managed and accepted very differently in the mining industry. The project 

investigating DPF systems should have been seen sooner by the mine as an eventual 

process not just for DPF systems but for diesel emissions control. A diesel emissions 

control process would comprise gauging performance of engines, emissions control 

systems, tailpipe emissions quality and ambient air quality. 

Monitoring the performance of DPF systems within a process does not necessarily 

require elaborate instrumentation for precision and accuracy. Instrumentation for the field 

should be chosen more on the priority of reliability and repeatability than precision and 

accuracy. There are integrated measurement systems such as the engine control modules 

(ECM) on electronic engines that should be given priority on verifying and monitoring 

performance. Auxiliary or add-on systems for monitoring exhaust backpressure and 

temperature are most often prone to failure and unreliable for underground mining 

equipment. The most reliable instrument for monitoring exhaust backpressure is still a 

simple mechanical gauge in the operator’s compartment on the vehicle. Whether it is a 

gauge, an indicator warning light, or an automatic shut down, the system is only as good 

as the operator that sits in front of it and interprets the information. Acquiring exhaust 

temperature profiles for duty cycles can be done with small, proven and reliable single 

channel dataloggers that are commercially available from most instrumentation suppliers. 

These are only required for building duty cycle profiles of engines and vehicles so these 

small portable instruments work well. The exhaust temperature and backpressure loggers 

used during the project had a high level of complexity with too many sensors and features 

which made them prone to failure. The UGAS emissions testing system used throughout 

the project proved to work reliably in verifying gaseous and particulate tailpipe 

emissions. It was and continues to be used by many mechanics on a regular daily basis 

for verifying emissions performance. The test developed using the ECOM analyzer for 

measuring carbon content with NIOSH method 5040 worked well for a periodic test of 

DPF efficiency when higher precision was required. Though not always practical and 

prone to interference factors, sampling and analysis of ambient DPM concentrations 

demonstrated to be a good method of cross-referencing the efficiency of DPF systems. 

Sampling operator exposures on specific vehicles equipped with DPF systems can 

provide a good cross reference to tailpipe emissions and efficiencies when interference 

factors such as other vehicles are minimized. 

One objective of this study was to estimate the costs associated with different DPF 

systems. However, although the mine attempted to track costs associated with the project, 
- 87 - 

not all costs were captured, and it was difficult to attribute some costs to specific DPF 

systems. 

This project brought together researchers, engine, vehicle, fuel and emissions control 

manufacturers, and most importantly the people from Brunswick Mine to select, 

implement and test these DPF systems. Participants came from Canada, the United States 

and Switzerland to work in the project. Much of this participation is based in Canada 

which has assisted in building a critical expertise based in Canada that can continue 

implementing this technology with the Canadian mining industry into the future. 

The future of DPF systems technology and making it work successfully in underground 

mining will rely heavily on this type of strong collaboration. The technology remains a 

long way from being an off-the-shelf or plug-and-play type of solution. Applications will 

remain mostly retrofits on existing vehicles which require a good deal of application 

engineering in every case regardless of whether retrofit or factory built. This same level 

of collaboration will be required with specifications built between the mine users, vehicle 

and engine manufacturers, and a consensus on how to build measure and maintain the 

success that this technology is capable of delivering. 

RREEECCCOOOMMMMMMEEENNNDDDAAATTTIIIOOONNNSSS

The following recommendations are directed towards anyone who might be responsible 

for, or involved in successfully implementing DPF technology on underground diesel 

mining equipment. 

Selection 

The selection process is a critical factor in successful implementation. Unfortunately, 

there is no current off-the-shelf DPF technology that can be easily plugged into mine 

vehicles and set to work. Mine staff must accurately map vehicle duty cycles and exhaust 

temperatures of vehicles they plan to outfit with DPF systems, and then use this data in a 

specification document or request for proposals to DPF manufacturers. 

Installation 

In most cases, DPFs will be installed as retrofits to vehicles. The DPF manufacturer 

should be asked to provide a complete retrofit kit including the associated hardware for 

matching to the engine and vehicle. This would include frame and guard modification 

hardware and proper piping along with appropriate mechanical flanges and flex couplings 

that will sustain operation without being prone to leaks. A critical component to the 

retrofit kit is properly interfaced controls for monitoring exhaust backpressure and 

temperature. Manufacturers of electronic engines now have the capability of interfacing 

these parameters with the existing engine electronic controls. This avoids the need for 

auxiliary monitoring systems which tend to require a great deal of maintenance. 
- 88 - 

Measurement 

The successful application of DPF technology requires emissions measurement systems 

that can be used in everyday operations by mine employees. There are many 

commercially available field ready measurement technologies that accommodate 

monitoring of undiluted DPM and gaseous emissions, exhaust backpressure and 

temperature, and monitoring of DPM in ambient concentrations. It is critical that all of 

these points are measured accurately and regularly by mine employees. 

Maintenance 

DPF technology requires heightened awareness from a maintenance perspective. This 

means paying close attention to the condition of the entire system, as well as ensuring 

that the measurement systems are properly maintained. Condition based maintenance 

decisions need to be made on accurately measured conditions. False or defective 

measurements due to improperly maintained instrumentation may result in maintenancebased failures of DPFs. Qualitative evaluation of system performance is also important 

and should be included in a well-designed DPF maintenance process. Qualitative 

evaluation includes visual inspections and monitoring conditions such as exhaust leaks. 

Verification 

Performance of DPF systems needs to be verified and cross checked by several criteria. 

Verifying the operation of a DPF by end-of-pipe exhaust measurements alone can lead to 

mistaken confidence in the functioning of the system. Performance should be cross 

checked and verified by DPM sampling in ambient concentrations as well as close 

monitoring of operators reports. The high capital investment of DPF systems, combined 

with the high impact potential for DPM reduction should justify a verification database at 

the mine that combines these factors and is reported on a regular basis. 
- 89 - 

RREEFFFEEERRREEENNNCCCEEESS

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