graham o’brien, csiro, csiro’s coal logistics findings
DESCRIPTION
Graham O'Brien delivered the presentation at 2014 Bulk Materials Handling Conference. The 11th annual Bulk Materials Handling Conference is an expert led forum focusing on the engineering behind the latest expansions and upgrades of bulk materials facilities. This conference will evaluate the latest engineering feats that are creating record levels of throughput whilst minimising downtime. For more information about the event, please visit: http://www.informa.com.au/bulkmaterials14TRANSCRIPT
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CSIRO’s Coal Logis/cs Findings
GRAHAM O‘BRIEN
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What we do: our domain focus
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Australian Coal Industry Overview
World’s second largest exporter – about 28% of world coal market
2010-2011 Coal production
raw black coal: 454Mt saleable black coal: 345Mt
Exports • 283Mt ($A44 billion)
Black and brown coal account for 75% of Australia’s electric power
Australia’s major resources and energy exports, 2010-11
CSIRO Coal Mining Research to maximise the benefits from Australia’s coal resources in an environmentally and socially responsible manner.
Research Stream Scope
Mining engineering Development of new mining systems, design and operational control techniques
Mining automation Development of automation of mining equipment, sensing and communication systems
Mine environmental technologies
Development of new mining environment mitigation methods and remedial techniques
Coal processing and Logistics
Development of new coal cleaning methods and rail and port engagements.
Largest coal mining research program in Australia
More than 70 CSIRO researchers
4 key research areas
Established a solid track record of success and delivered significant benefits
Mining ROM/CPPP Loadout Transport Port Ship Issues that have been iden4fied are: • S"cky coal: Issues with transfer hoppers, conveyors, rail wagon loading and unloading, and shiploading and unloading. • Cost and efficiency, scheduling, op4mizing rail transport and port throughput • Environmental. Noise, dust, water, spontaneous combus4on.
Efficient material transfer is cri4cal at all parts of the coal chain. Our coal logis4cs ini4a4ve specifically focuses on issues from rail loadout through to shiploading.
Trains are loaded for transport to the coal ports. Coals which give problems during unloading are known colloquially as s/cky coals.
Non s4cky coals unload well from boPom dump rail wagons.
S4cky coals give hang up which impedes unloading
Loading method and loadout design contributed to coal hangup during unloading.
Loaded with a front end loader Loaded with an impact loader
The RG Tanna Coal Terminal (Gladstone) determined that many mines provided s4cky coal products. In 2005 GPA es4mated that s4cky coal cost approximately 2% of port throughput (approximately 800,000 tonnes/ year). Other QLD coal ports had similar issues with s4cky coal.
Factors Outside of GPA Control
Wagon Design (134tph)
Waiting Dozers
Relocate Tripper
Sticky Coal
Barcode Resolution (wrong barcode, no barcode, damaged barcode)
Split Trains
QR Delays
Incorrect Mine Advice
Train Speed
GPA Can Influence by
GPA can Control:- Correct unloading procedure, skill levels, automation, design, allocation of responsib. System performance - delays of 60%
Electronic barcode
Reporting weekly to QRMonitoring, partnering
Scheduling
Scheduling
Monitor/reportReporting
Ploughing
Electronic data transfer
14% (218tph)
10%
6% 8%
1%
1%
Average of 660tph per split connote
5 Percent of trains jack hammered by mine
Jackhammer Trains by Mine 2003/2004 Start Train/End Train
HJ Roll.1%
Callide0%
SBW6%
Gregory4%
Yarrabee10%
Moura2%
Kestral5%
Oakey Crk1%
Ensham10%
Cook3%
BlackWater11%
Curragh24%
Jellinbah23%
What makes some coal s/cky?
Coal properties? (moisture, fines, ash content)
Wagon design? (slope sheet angle, door width, wall material)
Loading forces? (loading method, drop height)
Travel forces? ( vibration, travel time, adverse weather)
Field and laboratory work was conducted to identify and quantify these factors. This work was supported by the coal producers, Qld Rail and the coal ports.
Quantifying coal handleability- laboratory testing
Consolidating pressure (t/m2)
0 2 4 6 8 10 12
Dis
char
ge (k
g)
0
10
20
30
40
50
A B C D E F.2 (PP) G1 H1 (thermal) H2 (PCI)
Free flowing coalsSticky coals
Lab scale test which uses approx 90 kgs of coal replicates the arches formed in full scale wagons. It enables us to benchmark coals and determine size and moisture effects.
We developed a laboratory scale and a pilot scale test for assessing coals.
Centre sill
Coal arch
Acoustic Measuring devices
Video camera
Arch profile in a rail wagon. Arch profile in CSIRO lab scale test unit.
The lab test unit shows same arch profile as observed in rail wagons
Issues associated with the unloading of coal wagons are quite complex. To develop solutions to complex problems require buy in from all parties. To a large extent this was achieved for this research. Sticky coal is currently less of an issue than it was previously. Changes made at one position in the chain can impact on other links in the chain. New coals with different properties will come into the system in the next few years. Unknown at this stage is whether they will be sticky.
Project findings
Remnant Coal Detec/on
Undesirable residual coal in the wagons of emp4ed coal trains • Reduced capacity of coal wagons –reduced produc4vity
• Causes cross-‐contamina4on of coal with other mines: poten4ally reject wagons
• Dries out eventually, causing coal dust pollu4on from the trains
• Coal can jam in the wagon doors, leading to spills and derailments
• Large coal “hangups” can occur: the load fails to dump, hanging in a bridge that breaks later, causing spillage and poten4al derailment
1. RCD is a system that monitors coal train wagons, looking for coal hangups (currently installed on two dump sta4ons at GPC—R G Tanna).
2. GPC have also given considera4on to a proposed future automa"c cleaning system, with remote operator supervision, will engage the jackhammers to clear the detected hangup.
Remnant Coal Detec/on System
Remnant Coal Detec/on Enabling Technology for Detection & Measurement
• Several eye-safe commercial options
• Single-point laser scans using a rotating mirror to develop a 2D line
• Movement of target can create a 3D profile
Remnant Coal Detec/on
Remnant Coal Detec/on
Port efficiency: As the port is area constrained they need to maximize the use of their footprint. Also shown are dust monitoring sites.
We are currently undertaking a Laser Stockpile Mapping Trial at the R.G. Tanna Coal Terminal to assist them to op/mise the use of their footprint, and hence improve annual port capacity.
The low reflectivity of coal is a major limitation on the use of conventional laser range measurement systems for mapping coal stockpiles.
Modeling is an important tool for op4mizing material transfer opera4ons.
Computa4onal Modelling Applica4ons in Coal Transport and dust genera4on.
This work was done by Paul Cleary’s research group in Melbourne.
Presenta4on 4tle | Presenter name
Coal Discharge from Rail Wagons
Coal transport from mine to terminal is vital to Na4onal Coal Industry.
The unloading 4me for a single wagon constrains the rate at which coal can be delivered.
• Discharge 4me depends on coal flowability which depends on: – par4cle size distribu4on – par4cle shape distribu4on – material proper4es – cohesive forces between wet coal
Improvements in rail wagon design require deeper understanding of the interac4on between granular coal mass and the internal geometry of the wagon.
Coal Discharge from Rail Wagons
Bradken Rail Wagon Design
Dimensions of a single wagon – Height = 3.7 m
– Length = 14.6 m
– Width = 3.0 m
5 compartments, 8 doors which are scheduled to open in pairs
Coal unloads while the train is in mo4on. – Adjacent pairs of doors are triggered to open mechanically in a coal terminal by a fixed mechanism beside the rail line.
– The 4me interval between each set of doors opening is determined by the speed of the train through the terminal.
Coal Flow in Rail Wagons
DEM Coal par5cles Real coal mass with a top size of 50 mm was modelled using cohesive, oversized 80 mm DEM par4cles
485,000 par4cles
DEM superquadrics – Shape distribu"on: 3.0 – 6.0 – Aspect ra"os from 0.5 – 1.0
A cohesion Bond number of 0.5 was used (based on comparison between a 50 mm DEM simula4on and pilot hopper experiments)
Pairs of wagon doors were scheduled to open at 6 s intervals
Coal Discharge from a Rail Wagon
• Sloping end walls provide strong resistance to flow. End compartments slower to fully discharge than inner compartments
• Considerable flow between compartments around and through the baffles. Preferential central flow through each door with coal mass retarded at walls.
• In the inner compartments, active regions of rapid coal flow are observed to extend from discharging door up to the coal surface
Dust dispersal modelling on a conveyor chute using a coupled discrete element and CFD method, CFD 2011, Trondheim, June 2011
Model – Physically realis4c dust model – Based on experimentally derived expression
Computa4onal method – Combined DEM/CFD method
Dust Modelling
Par4culates comes from many different sources: • Natural sources
– sea spray – animal and plant maPer – wind blown stone dust – wildfires – etc.
• Human sources – Mining ac4vi4es – plas4c and paint – fuel combus4on – rust – etc.
Introduc/on to Air Par/culates (Dust)
200µm
10µm
Mackay Ports • Part of a large study being conducted • Assisted a coal producer address a community complaint
Newcastle • Assessment of rou4ne samples • Assessment of compliance samples Gladstone • Assisted with Port community complaints
Brisbane • Assisted with community concerns
Current studies
http://en.wikipedia.org/wiki/File:Australian_Energie_ressources_and_major_export_ports_map.svg
Air Par/culates – Size Does Mafer
Gets trapped by the body’s
natural defense mechanisms
Does not enter body
Small enough to enter the airways
Gets trapped in the lungs
Small enough to enter the blood
vessels
Gets deposited around the body in various organs
Nuisance Dust SePles quickly and can easily be
seen
Respirable Dust Stays suspended for a long 4me and
is too small to see
Smaller than 2.5 microns Small than 10 microns
Typically of industrial origin
Total airborne
par/culates
Bigger than 10 microns
Typically of natural origin
“Dust” PM10 PM2.5
Category
Technical Name
Size
Origin
Health Implica/ons
• 14 bit colour images are collected using an air lens
• Images are mosaiced together to provide detail on mul4ple complete par4cles.
• Depending on magnifica4on used 1 pixel in the images represents 0.32 or 0.12 microns.
• This provides informa4on on each individual par4cle in the sample.
CSIRO’s Coal Petrography Laboratory uses op4cal reflected light micro.scopy for the analysis of dust samples
50µm
Unidentified Mineral
Coal
Soot
Paint
50µm
Unidentified Mineral
Coal
Soot
Spore
2 images collected as part of a study of dust from the Mackay region
0
2
4
6
8
10
12
14
0.20 0.30 0.40 0.50 0.60 0.70 0.80 0.90 1.00 1.10 1.20 1.30 1.40 1.50 1.60 1.70 1.80 1.90 2.00 2.10
%
Random Vitrinite Reflectance (%)
Reflectance histogram of the coal particles indicate that the coal dust came from multiple sources
Analysis of a Dust Sample from Mackay Image Collec/on
500µm
50µm
100 Images mosaiced together covering an area of 4.5x3.5 mm
Analysis of a Dust Sample Original Image
Analysis of a Dust Sample Characterised Image
Coal Non-coal
Par/cle informa/on
Image Characterised image Area (pixels)
Area (um)^2
Particle width (um)
Particle length (um) Grain Class
227 23.2 4 10 non-coal 1055 108.0 11 16 non-coal 475 48.6 7 10 coal 621 63.6 7 13 non-coal 24113 2469.2 49 85 non-coal 297 30.4 6 10 non-coal 1871 191.6 14 21 non-coal 9015 923.1 32 48 coal 3024 309.7 20 31 non-coal 348 35.6 6 13 non-coal 284 29.1 6 10 non-coal 1090 111.6 12 13 non-coal 1085 111.1 11 25 non-coal 235 24.1 5 8 non-coal 1026 105.1 11 24 non-coal 1613 165.2 12 23 non-coal 360 36.9 6 9 non-coal 3762 385.2 24 36 non-coal 6046 619.1 24 55 non-coal 1361 139.4 13 19 non-coal
Results of Analysis by Size (volume %) SIZE AMOUNT COAL AMOUNT NON-‐COAL TOTAL NUMBER OF GRAINS
PM2.5* (>2.5um)
0* 0* 0* 10*
PM10 (2.5><-‐10um)
1 18 19 8155
Nuisance Dust (>10um)
3 78 81 4667
Total 4 96 100 12832 *Limited data available on -‐2.5 micron par4cles as images were collected with 20x lens
• Coal only 4% of the sample • Only ¼ of the coal present <10micron • More than 80% of the sample is nuisance dust (greater than 10 micron) • Limited data on the >2.5micron at 200x magnifica4on • Results validated through manual point coun4ng
Size distribu/on of par/cles
0
10
20
30
40
50
60
<2.5 2.5<10 10<30 30<60 60<100 100<140
Volume %
Size (microns)
Size Distribu/on
coal
non-‐coal
Analysis of a Dust Sample from Brisbane Image Collec/on
Over 100 mages collected of 3mm diameter circle containing sample
• Informa4on determined on in excess of 2000 par4cles
• Less than 1% of par4cles iden4fied as coal
• Reflectance values for the coal par4cles was around 0.5% – This is consistent with literature values for low rank thermal coals from West Moreton Coal Fields which are railed through Brisbane to the Port of Brisbane
• Majority of non-‐coal par4cles appeared to be soot with a median size of 20µm
Results of Analysis – Brisbane Sample
Analysis of a Dust Sample Example Par/culates at 200x magnifica/on
50µm
Mineral
Coal
Soot
Quartz
50µm
Unidentified Mineral
Coal
Soot
Spore
Analysis of a Dust Sample Example Par/culates at 500x magnifica/on
10µm
Coal
Mineral
Flyash
Plastic
Coal
Paint
10µm
Mineral
Non-‐Coal Total No of
grains Size class Grain class Coal Fly ash Soot Bright Minerals
Dark Minerals Unidentified
Nuisance +30 13.9 0.1 0.3 0.0 1.0 0.0 15.3 58 Nuisance -‐30 + 10 45.0 0.3 0.0 0.0 3.8 0.0 49.1 1056 Inhalable -‐10 + 2.5 28.4 0.0 0.0 0.0 5.2 0.0 33.6 6449 Respirable -‐2.5 1.6 0.0 0.0 0.0 0.4 0.0 2.0 1883 Total 88.9 0.4 0.3 0.0 10.3 0.0 100.0 9,446
Example image (one of about 2,000) collected during the analysis of a sample of dust from a sampling station at a coal port.
Non-‐Coal Total No of
grains Size class Grain class Coal Fly ash Soot Bright Minerals
Dark Minerals Unidentified
Nuisance +30 0.0 0.0 0.0 6.7 29.9 1.9 38.5 61 Nuisance -‐30 + 10 0.1 0.2 0.1 20.1 28.4 1.3 50.1 535 Inhalable -‐10 + 2.5 0.1 0.0 0.0 3.4 7.3 0.0 10.9 1260 Respirable -‐2.5 0.0 0.0 0.0 0.1 0.5 0.0 0.5 333 Total 0.2 0.2 0.1 30.2 66.2 3.1 100.0 2,189
Example image (one of about 2,000) collected during the analysis of a sample of dust from a sampling station a distance from the coal port.
To improve the safely and efficiency of coal transporta4on from mine to port and onto markets in a socially responsible manner which has zero environmental impact, requires commitment from all stakeholders.
We believe that applied research is an important component for obtaining incremental improvement for exis4ng opera4ons and step change improvement for greenfield opera4ons.
Conclusions
Graham O'Brien CSIRO Energy Flagship Stream Leader-‐ Enhanced Coal Cleaning and Logis/cs Queensland Centre of Advanced Technologies 1 Technology Court phone +61 733274457 Pullenvale 4069 mobile 0417612374 Brisbane QLD Australia Graham.O’[email protected]
Thank you.
Questions?