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The European Organisation for the Safety of Air Navigation
EUROCONTROL โ€“ Univ. Politehnica of Bucharest
& ROMATSA Project
Volcanic Ash Safety
presented at ICAO IVATF, Montreal, 11-15 July 2011
Ash Safety
Prof. dr. ing. C. BERBENTE
S.l. dr. ing. mat. A. BOGOI
Conf. dr. ing. T. CHELARU
S.l. drd. Ing. C. E. CONSTANTINESCU, MBA
Prof. dr. ing. S. DANAILA
D. DIMITRIU, PhD
Drd. Ing. V. DRAGAN
S.l. dr. ing. D. D. ISVORANU
E. HALIC, M.D.
S.l. dr. ing. L. MORARU
Conf. dr. dr. ing. O. T. PLETER, MBA
As. drd. A. RAJNOVEANU, M.D.
Prof. dr. ing. V. STANCIU
Conf. dr. ing. M. STOIA-DJESKA
Drd. Ing. D. C. TONCU
R. ULMEANU, M.D. PhD
Studies on the Measurement and the Effects
of the Volcanic Origin Particles in Suspension in the Atmosphere
on the Safety of Aircraft
Ash Safety
Presentation Title Ash Safety Research Results
Version / Date / Author 1.1 / 1.07.2011 / OTP
Beneficiary EUROCONTROL
Keywords volcanic ash, volcanic dust, sand
aerosols, impact on aviation, impact on
flow management
4
Presentation Overview
1.Introduction โ€“ research subject, objectives, and
relevance
2.Risks, vulnerability, and the scale of the phenomenon
3.Ash vs. Dust; sand aerosols; why does particle size
matter?
4.Extent of the danger area: volcanic ash cloud estimation
5.Human health effects
6.Concentration measurement and forecasting
7.Selected conclusions
5
โ€ข Research Subject
โ€žStudies on the Measurement and the Effects of the
Volcanic Origin Particles in Suspension in the Atmosphere
on the Safety of Aircraftโ€
โ€ข Research Objectives: to provide objective, relevant, and
scientifically validated information for the future
decisions on the air traffic in volcanic ash contaminated
atmosphere, for the best trade-off for the most fluent air
traffic under the circumstances, with uncompromised
flight safety.
Ash Safety Project was triggered by Eyjafjalla
6
Read the Scientific Report to find that โ€ฆ
โ€ข Visible volcanic ash cloud is dangerous to aviation, but
it does not travel very far (1-200 NM, max. 550 NM down
the wind in the greatest eruption in history, Pinatubo
1991);
โ€ข Volcanic dust contamination in concentrations
comparable to that current for sand aerosols (4โˆ™10โ”€3
g/m3
) is not a safety issue and rather a maintenance
issue (like flying at Ryadh or Cairo);
โ€ข Tactical avoidance of volcanic dust contamination
based on on-board instruments is not practical;
7
โ€ข Worries about volcanic ash/dust contamination impact
on the human respiratory system of the occupants of
an aircraft are not justified;
โ€ข Volcanic Ash/Dust Concentration is a noisy random
variable, very difficult to measure with certainty and
consistency; the concentration measurements should
be averaged on a cubic hectometre scale (1,000,000 m3
;
the hectometric principle);
โ€ข Concentration measuring unit: 1 kg/hm3
= 10โˆ’3
g/m3
Read the Scientific Report to find that โ€ฆ (2)
8
โ€ข Volcanic Dust Concentration is less important than the
size distribution of particles; volcanic dust particles
resulting from differential sedimentation in the natural
atmospheric dispersion process do not cause abrasion
and/or glass deposits inside the turbofan engine,
regardless the concentration;
โ€ข The best option to address volcanic ash/dust problems
in the future is a quick reaction algorithm to estimate
volcanic ash cloud and a prediction based on an Euler
dispersion model with data assimilation from hectometric
in-situ sensors
Read the Scientific Report to find that โ€ฆ (3)
9
Parts / Occupants Cause Effect Response
Turbine engines fuel injection and combustor
deposits of melted ash (glassy
coatings)
surge, shut-down, difficult
restart in flight
idle thrust, evasive maneuver
Turbine engines clogging the turbine cooling
vents
overheating idle thrust, evasive maneuver
Pitot-static clogging the sensors unreliable air speed
indications
attitude-based flying,
indicated air speed deducted
from ground speed and wind
velocity
Turbine engines abrasion with hard particles wear of fan, compressor,
turbine, transmission
idle thrust, evasive maneuver
Pneumatic controls clogging the vents failure evasive maneuver
Windshield, body,
wings, empennage
cracks, abrasion with hard
particles
wear, opaqueness evasive maneuver
Avionics, on-board
instruments
clogging air-cooling vents,
electrostatic discharges
overheating, malfunction evasive maneuver
Human occupants breathing contaminated air,
eye cornea contact with
ash/dust particles
respiratory problems, eye
damage
nose breathing, replace
contact lenses with eyeglasses
Turbine engines, body
and instruments
metallic parts
acidity, exposure to associated
SO2 and sulfurous acid
corrosion (in time) maintenance check and
replacement
What can go wrong in a VA encounter
10
Air Breathing Order
of Magnitude
Description Affected Hardware
or Liveware
1,000 m3
/s High flow non-filtered
air breathing
turbine engines
100 m3
/s Directly exposed to
airflow
windshield,
empennage, body
and wing
0.01 m3
/s Low flow non-filtered
air breathing
human occupants,
Pitot-static sensors,
computers, electrical
engines and other air-
cooled parts
Irrelevant Air breathing through
filters
piston engines, air-
cooled parts with air
filters
Vulnerability ~ Air Breathing Flow
11
Turbofan engines are huge vacuum cleaners, sucking an average
of 1,000,000 m3
= 1 hm3
each in 10 minutes of flight
The Silica particles in the core flow will
be deposited as glass in the
combustion chamber and on the HPT
One kilogram of deposits is enough
to cause turbine overheating and
even engine failure (restarting is
possible though outside the contaminated area)
Vulnerability is Critical for Turbofan Engines
12
Characteristic time scope = 10 minutes of flight = exposure of an
average turbine engine to 1,000,000 m3
= 1 hm3
of air
10 minutes is the maximum exposure of an aircraft engaged in an
evasive manoeuver after an unanticipated volcanic ash
encounter
Scale of phenomenon = 1 Cubic hectometre
13
Example of quantity of contaminant
accumulated in 10 minutes of flight in a
concentration of 2โˆ™10โ”€3
g/m3
Air Breathing Order of
Magnitude
Quantity of contaminant
accumulated in 10 minutes
flight at a concentration of
2โˆ™10 3โ”€
g/m3
Affected Hardware or Liveware
1,000 m3
/s 1.2 kg turbine engines
100 m3
/s 120 g windshield, empennage, body
and wing
0.01 m3
/s 12 mg human occupants, Pitot-static
sensors, computers, electrical
engines and other air-cooled
parts
Irrelevant 0 g piston engines, air-cooled parts
with air filters
Terminology discriminator:
Volcanic Ash = 1/16 mm โ€“ 2 mm
(Coarse ash)
Volcanic Dust < 1/16 mm
(Fine ash)
Volcanic Ash Volcanic Dust
Particle size (ยตm) 63 - 2000 < 63
Location 1-200 NM around the
volcano
Floats around the
world
Sedimentation time โ‰ˆ 1/2 hour (for 1 mm) 23 Days (for 10ยตm)
14
15
Volcanic Dust ฯ† < 1/16 mm
(Fine ash)
Volcanic Ash ฯ† = 1/16 โ€“ 2 mm
(Coarse ash)
Ash vs. Dust
16
Volcanic Dust Haze
(Contamination)
Thin layers of dust
only visible from selected
viewing angles or from a
far distance e.g. satellite
Volcanic Ash Cloud
Cloud clearly visible to naked
eye from all angles,
clear boundary
Visible Volcanic Ash Cloud vs. Volcanic Dust
Contamination
17
Eruption Case Study: H=10 km, W=50 kts
Falling
speed (m/s)
from:
1 mm (ash) 100 ยตm
(ash)
10 ยตm
(dust)
1 ยตm (dust)
10,000 m 6.0 0.8 0.005 8ยท10โˆ’5
8,000 m 5.7 0.7 0.005 8ยท10โˆ’5
6,000 m 5.5 0.7 0.005 7ยท10โˆ’5
4,000 m 5.3 0.7 0.004 7ยท10โˆ’5
2,000 m 5.1 0.6 0.004 7ยท10โˆ’5
Average
falling
speed (m/s)
5.5 0.7 0.005 7ยท10โˆ’5
Ash: Dust
1/16 mm
= 62.5 mm
Ash:
visible,
dangerous,
local / short term
Dust:
Less threatening,
globe trotter /
long term
1 mm (ash) 100 ยตm (ash) 10 ยตm
(dust)
1 ยตm (dust)
Number of particles in 1 m3
at a
concentration of 2โˆ™10โˆ’3
g/m3
(2
kg/hm3
)
3 2,728 2,728,370 2,728,370,453
18
1 mm
(ash)
100 ยตm
(ash)
10 ยตm
(dust)
1 ยตm
(dust)
Sedimentation Time (h) 0.5 4.0 555.6 39,682.5
Distance travelled (NM) 25 200 27,780 1,984,125
Sand Blasting Effect on Particle Size
Effects of particle impact velocity and particle size on substrate roughness, from Weidenhaupt, W., 1970, รœber den EinfluรŸ
der Entzunderungs- und Ziehbedingungen auf die, Oberflรคchen-Feingestalt von Stab- und Profilstahl, Dissertation, RWTH
Aachen, Germany. as referenced by Momber, A., 2008, Blast Cleaning Technology, Springer
20
Abrasion Caused by Ash vs. Dust
Ash follows airflow streamlines imperfectly and impacts
walls: inertial forces > aerodynamic forces
Dust follows airflow streamlines:
inertial forces << aerodynamic forces
21
Glass Coating / Clogging by Ash vs. Dust
22
Relative Safety Risk vs. Size: 0.1-1000 ยตm
(qualitative representation)
23
Highest-Risk Dust Particle Segment: 1-10 ยตm
Turbofan engines (tests on simulated engines):
Larger> The turbofan functions like a centrifugal separator
(no issue with the volcanic ash/dust in the by-pass flow)
Smaller> Particles exit the engine without touching any wall
Human respiratory system:
Larger> filtered by body barriers
Smaller> get out with expiration
(not retained in the lungs)
Volcanic Ash / Dust / Sand Aerosols
Volcanic Ash Cloud Volcanic Dust
Contamination
Sand Aerosol
Contamination
Visibility Clearly visible from all
angles, easily
identifiable by dark
colour, distinct
boundary
Visible only from
selected angles,
hard to distinguish,
visible in satellite
imagery
Visible sometimes
from selected
angles, visible in
satellite imagery
Where? Within 1-200 NM of the
eruption up to 500 NM
Very large areas
(>1000 NM in size)
Large areas
Typical
Concentrations
(1 kg/hm3
=
10โˆ’3
g/m3
)
1000 kg/hm3
1-100 kg/hm3
1-100 kg/hm3
Particle size
range (ยตm)
1-2000 1-40 1-50
Floatability in
atmosphere
(age)
12 Hours (due to ash-
dust differentiated
sedimentation)
6 Days (traces
remain for years)
3 Days
24
Volcanic Ash
Cloud
Volcanic Dust
Contamination
Sand Aerosol
Contamination
Aviation Safety
Risk
Serious
incidents, no
injury accidents
None on record None
Impact on
aviation
Local Global due to
misinterpretation
Maintenance
issues
Source: Prof. Ulrich Schumann, DLR Institute of Atmospheric Physics, NASA Earth Observatory
25
26
Severity vs. Frequency Safety Risk
16/02/2007 = 14 aircraft: windshield failures within 3ยฝh
19/01/2011 = 3 aircraft: windshield failures within ยฝh
27
Ash-Sized Sand โ€“ a New Safety Concern (Denver, CO)
Source for photos: www.airliners.net
Skywest Canadair CRJ-700 on behalf of
United Airlines, flight OO-6761/UA-6761
from Denver, CO to Cleveland, OH (USA),
reported a cracked windshield during initial
climb out of runway 34R and returned to
Denver .
Skywest Canadair CRJ-200 on behalf of
United Airlines, registration N978SW
performing flight OO-6576/UA-6576 from
Denver, CO (USA) to Winnipeg, MB
(Canada), reported a windshield cracked
during initial climb out of runway 34L and
returned to Denver
Delta Airlines Boeing 757-200, flight
DL-1916 from Denver, CO to Atlanta,
GA (USA), during initial climb out of
runway 34L reported a cracked
windshield and returned to Denver
28
Future Eruption First Reaction
Checklist
๏ƒผ Location of the eruption / time: LAT, LONG, HHMMz,
DDMMYY
{repeat until eruption ends}
๏ƒผ How tall is the eruption column? ECH (m AMSL)
๏ƒผ Download wind profile in the area (e.g. from NOAA): WD/WV
๏ƒผ Calculate how far will the volcanic ash cloud go: VAMAX
๏ƒผ Draw a contour with VAMAX as major axis on the map: DA
Ash4D
29
Volcanic Ash Danger Area
Shape: defined by the variability of wind direction and
amplitude of wind velocity
30
Volcanic Ash Danger Area
How far does the VA travel?
Function of: H (height of eruption column), FL (flight
level), and WV (wind velocity)
Eruption
column H (m) 30000
Flight Level (100 ft) 100
Wind Velocity (kts) 50
Danger area (NM) 535
Pinatubo 1991
Eruption
column H (m) 9000
Flight Level (100 ft) 100
Wind Velocity (kts) 100
Danger area (NM) 236
Eyjafjalla 2010
Eruption
column H (m) 3500
Flight Level (100 ft) 30
Wind Velocity (kts) 20
Danger area (NM) 21
Etna 2011
31
Why 500 NM for Pinatubo = 250 NM for Eyjafjalla?
Slide from Jacques Renvier, CFM/SNECMA, Atlantic Conference on Eyjafjallajokull, Keflavik 2010
32
Why 500 NM for Pinatubo = 250 NM for Eyjafjalla?
(Kilauea, Hawaii
28 years continuous eruption)
33
Conclusions on Human Health Effects
What was studied: passengers (short-term) and crew (long-
term) exposure to volcanic dust concentrations of 4โˆ™10โ”€3
g/m3
โ€œWell under limits for short time exposure and even lower
than those for chronic exposureโ€
โ€œReasonable to anticipate no risk for silicosis or lung cancer
in passengers and crew membersโ€
โ€œConcentration lower than environmental Silica aerosols in
some parts of the world (e.g. Ryadh, Cairo)โ€
34
Concentration: volatile, noisy, measured
indirectly
Direct and consistent methods to measure
concentration in real time: none
Indirect methods, subject to large methodical errors and
measuring historical values of concentration along a
line of sight/movement:
โ€ข In-situ sampling;
โ€ข Ground up-looking LIDAR;
โ€ข Airborne down-looking LIDAR;
โ€ข Ground optical photometre;
โ€ข Satellite infrared image.
35
Concentration measurement problems: 1. scale of
phenomenon and 2. consistency
All these technologies deployed in the same area would
yield different results
36
Hectometric Principle: Why do concentration
measurements require averaging at the 1 hm3
scale?
In this example we assume we
want to measure the brightness
of a halftone image
37
Future sensors are shortsighted and the scale of
the phenomenon is larger
38
Types of concentrations Actual Measured Forecasted
Blindly (open-
loop)
Forecasted with
Data
Assimilation
When they are available (hours) never T+2H Tโˆ’18H (up to
Tโˆ’180H)
Tโˆ’18H (up to
Tโˆ’180H)
Uncertainty due to initial data of
the eruption (orders of magnitude)
- - 2 - 3 0.2 - 1
Uncertainty due to the Eulerian
diffusion model (orders of
magnitude)
- - +1 every 24
hours
0.1 - 0.4
Uncertainty due to the
measurement techniques
- 0.1 โ€“ 1 - -
Area coverage - Very local1
Global Global
Overall errors 0 Significant Very large and
rapidly
increasing in
time
Large
Relevance to IFR flight operations - Tactical
avoidance
Flight planning Flight planning
Relevance to ATM - Forecasts
Validation
Airspace
management,
Flow
management
Airspace
management,
Flow
management
[1]
Except the satellite images,
which provide a global view
Airborne in situ hectometric concentrationโ€
measurement unit
isokinetic
39
VADHCMU
Volcanic Ash/Dust Hectometric Concentration
Measurement Unit
1. Airborne 6 channel (3 wavelengths plus polarizations)
backscattering infrared LIDAR,
2. Ground based (mobile) optical photometre, and
3. Airborne inโ€situ hectometric concentration
measurement unit.
A consistent and systematic measurement technology for
data assimilation:
40
41
Selected Conclusions
โ€ข Extending the term of volcanic ash cloud as per ICAO
Doc9691 to the volcanic dust haze is wrong and
misleading;
โ€ข Size of the particles matters more than concentration as
impact on aircraft and aircraft turbofan engines;
โ€ข Predicting concentrations using a dispersion model
with data assimilation from a systematic daily
measurement scheme using hectometric in-situ
samplers is the best choice for a way forward;
โ€ข Immediate reaction to a VA threat should be based on a
simple kinematic model of the extension of the volcanic
ash cloud and not on chasing the dust going round the
globe. Please, read the final report for more!
Vulcanic ash safety

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Vulcanic ash safety

  • 1. The European Organisation for the Safety of Air Navigation EUROCONTROL โ€“ Univ. Politehnica of Bucharest & ROMATSA Project Volcanic Ash Safety presented at ICAO IVATF, Montreal, 11-15 July 2011
  • 2. Ash Safety Prof. dr. ing. C. BERBENTE S.l. dr. ing. mat. A. BOGOI Conf. dr. ing. T. CHELARU S.l. drd. Ing. C. E. CONSTANTINESCU, MBA Prof. dr. ing. S. DANAILA D. DIMITRIU, PhD Drd. Ing. V. DRAGAN S.l. dr. ing. D. D. ISVORANU E. HALIC, M.D. S.l. dr. ing. L. MORARU Conf. dr. dr. ing. O. T. PLETER, MBA As. drd. A. RAJNOVEANU, M.D. Prof. dr. ing. V. STANCIU Conf. dr. ing. M. STOIA-DJESKA Drd. Ing. D. C. TONCU R. ULMEANU, M.D. PhD Studies on the Measurement and the Effects of the Volcanic Origin Particles in Suspension in the Atmosphere on the Safety of Aircraft
  • 3. Ash Safety Presentation Title Ash Safety Research Results Version / Date / Author 1.1 / 1.07.2011 / OTP Beneficiary EUROCONTROL Keywords volcanic ash, volcanic dust, sand aerosols, impact on aviation, impact on flow management
  • 4. 4 Presentation Overview 1.Introduction โ€“ research subject, objectives, and relevance 2.Risks, vulnerability, and the scale of the phenomenon 3.Ash vs. Dust; sand aerosols; why does particle size matter? 4.Extent of the danger area: volcanic ash cloud estimation 5.Human health effects 6.Concentration measurement and forecasting 7.Selected conclusions
  • 5. 5 โ€ข Research Subject โ€žStudies on the Measurement and the Effects of the Volcanic Origin Particles in Suspension in the Atmosphere on the Safety of Aircraftโ€ โ€ข Research Objectives: to provide objective, relevant, and scientifically validated information for the future decisions on the air traffic in volcanic ash contaminated atmosphere, for the best trade-off for the most fluent air traffic under the circumstances, with uncompromised flight safety. Ash Safety Project was triggered by Eyjafjalla
  • 6. 6 Read the Scientific Report to find that โ€ฆ โ€ข Visible volcanic ash cloud is dangerous to aviation, but it does not travel very far (1-200 NM, max. 550 NM down the wind in the greatest eruption in history, Pinatubo 1991); โ€ข Volcanic dust contamination in concentrations comparable to that current for sand aerosols (4โˆ™10โ”€3 g/m3 ) is not a safety issue and rather a maintenance issue (like flying at Ryadh or Cairo); โ€ข Tactical avoidance of volcanic dust contamination based on on-board instruments is not practical;
  • 7. 7 โ€ข Worries about volcanic ash/dust contamination impact on the human respiratory system of the occupants of an aircraft are not justified; โ€ข Volcanic Ash/Dust Concentration is a noisy random variable, very difficult to measure with certainty and consistency; the concentration measurements should be averaged on a cubic hectometre scale (1,000,000 m3 ; the hectometric principle); โ€ข Concentration measuring unit: 1 kg/hm3 = 10โˆ’3 g/m3 Read the Scientific Report to find that โ€ฆ (2)
  • 8. 8 โ€ข Volcanic Dust Concentration is less important than the size distribution of particles; volcanic dust particles resulting from differential sedimentation in the natural atmospheric dispersion process do not cause abrasion and/or glass deposits inside the turbofan engine, regardless the concentration; โ€ข The best option to address volcanic ash/dust problems in the future is a quick reaction algorithm to estimate volcanic ash cloud and a prediction based on an Euler dispersion model with data assimilation from hectometric in-situ sensors Read the Scientific Report to find that โ€ฆ (3)
  • 9. 9 Parts / Occupants Cause Effect Response Turbine engines fuel injection and combustor deposits of melted ash (glassy coatings) surge, shut-down, difficult restart in flight idle thrust, evasive maneuver Turbine engines clogging the turbine cooling vents overheating idle thrust, evasive maneuver Pitot-static clogging the sensors unreliable air speed indications attitude-based flying, indicated air speed deducted from ground speed and wind velocity Turbine engines abrasion with hard particles wear of fan, compressor, turbine, transmission idle thrust, evasive maneuver Pneumatic controls clogging the vents failure evasive maneuver Windshield, body, wings, empennage cracks, abrasion with hard particles wear, opaqueness evasive maneuver Avionics, on-board instruments clogging air-cooling vents, electrostatic discharges overheating, malfunction evasive maneuver Human occupants breathing contaminated air, eye cornea contact with ash/dust particles respiratory problems, eye damage nose breathing, replace contact lenses with eyeglasses Turbine engines, body and instruments metallic parts acidity, exposure to associated SO2 and sulfurous acid corrosion (in time) maintenance check and replacement What can go wrong in a VA encounter
  • 10. 10 Air Breathing Order of Magnitude Description Affected Hardware or Liveware 1,000 m3 /s High flow non-filtered air breathing turbine engines 100 m3 /s Directly exposed to airflow windshield, empennage, body and wing 0.01 m3 /s Low flow non-filtered air breathing human occupants, Pitot-static sensors, computers, electrical engines and other air- cooled parts Irrelevant Air breathing through filters piston engines, air- cooled parts with air filters Vulnerability ~ Air Breathing Flow
  • 11. 11 Turbofan engines are huge vacuum cleaners, sucking an average of 1,000,000 m3 = 1 hm3 each in 10 minutes of flight The Silica particles in the core flow will be deposited as glass in the combustion chamber and on the HPT One kilogram of deposits is enough to cause turbine overheating and even engine failure (restarting is possible though outside the contaminated area) Vulnerability is Critical for Turbofan Engines
  • 12. 12 Characteristic time scope = 10 minutes of flight = exposure of an average turbine engine to 1,000,000 m3 = 1 hm3 of air 10 minutes is the maximum exposure of an aircraft engaged in an evasive manoeuver after an unanticipated volcanic ash encounter Scale of phenomenon = 1 Cubic hectometre
  • 13. 13 Example of quantity of contaminant accumulated in 10 minutes of flight in a concentration of 2โˆ™10โ”€3 g/m3 Air Breathing Order of Magnitude Quantity of contaminant accumulated in 10 minutes flight at a concentration of 2โˆ™10 3โ”€ g/m3 Affected Hardware or Liveware 1,000 m3 /s 1.2 kg turbine engines 100 m3 /s 120 g windshield, empennage, body and wing 0.01 m3 /s 12 mg human occupants, Pitot-static sensors, computers, electrical engines and other air-cooled parts Irrelevant 0 g piston engines, air-cooled parts with air filters
  • 14. Terminology discriminator: Volcanic Ash = 1/16 mm โ€“ 2 mm (Coarse ash) Volcanic Dust < 1/16 mm (Fine ash) Volcanic Ash Volcanic Dust Particle size (ยตm) 63 - 2000 < 63 Location 1-200 NM around the volcano Floats around the world Sedimentation time โ‰ˆ 1/2 hour (for 1 mm) 23 Days (for 10ยตm) 14
  • 15. 15 Volcanic Dust ฯ† < 1/16 mm (Fine ash) Volcanic Ash ฯ† = 1/16 โ€“ 2 mm (Coarse ash) Ash vs. Dust
  • 16. 16 Volcanic Dust Haze (Contamination) Thin layers of dust only visible from selected viewing angles or from a far distance e.g. satellite Volcanic Ash Cloud Cloud clearly visible to naked eye from all angles, clear boundary Visible Volcanic Ash Cloud vs. Volcanic Dust Contamination
  • 17. 17 Eruption Case Study: H=10 km, W=50 kts Falling speed (m/s) from: 1 mm (ash) 100 ยตm (ash) 10 ยตm (dust) 1 ยตm (dust) 10,000 m 6.0 0.8 0.005 8ยท10โˆ’5 8,000 m 5.7 0.7 0.005 8ยท10โˆ’5 6,000 m 5.5 0.7 0.005 7ยท10โˆ’5 4,000 m 5.3 0.7 0.004 7ยท10โˆ’5 2,000 m 5.1 0.6 0.004 7ยท10โˆ’5 Average falling speed (m/s) 5.5 0.7 0.005 7ยท10โˆ’5 Ash: Dust 1/16 mm = 62.5 mm Ash: visible, dangerous, local / short term Dust: Less threatening, globe trotter / long term
  • 18. 1 mm (ash) 100 ยตm (ash) 10 ยตm (dust) 1 ยตm (dust) Number of particles in 1 m3 at a concentration of 2โˆ™10โˆ’3 g/m3 (2 kg/hm3 ) 3 2,728 2,728,370 2,728,370,453 18 1 mm (ash) 100 ยตm (ash) 10 ยตm (dust) 1 ยตm (dust) Sedimentation Time (h) 0.5 4.0 555.6 39,682.5 Distance travelled (NM) 25 200 27,780 1,984,125
  • 19. Sand Blasting Effect on Particle Size Effects of particle impact velocity and particle size on substrate roughness, from Weidenhaupt, W., 1970, รœber den EinfluรŸ der Entzunderungs- und Ziehbedingungen auf die, Oberflรคchen-Feingestalt von Stab- und Profilstahl, Dissertation, RWTH Aachen, Germany. as referenced by Momber, A., 2008, Blast Cleaning Technology, Springer
  • 20. 20 Abrasion Caused by Ash vs. Dust Ash follows airflow streamlines imperfectly and impacts walls: inertial forces > aerodynamic forces Dust follows airflow streamlines: inertial forces << aerodynamic forces
  • 21. 21 Glass Coating / Clogging by Ash vs. Dust
  • 22. 22 Relative Safety Risk vs. Size: 0.1-1000 ยตm (qualitative representation)
  • 23. 23 Highest-Risk Dust Particle Segment: 1-10 ยตm Turbofan engines (tests on simulated engines): Larger> The turbofan functions like a centrifugal separator (no issue with the volcanic ash/dust in the by-pass flow) Smaller> Particles exit the engine without touching any wall Human respiratory system: Larger> filtered by body barriers Smaller> get out with expiration (not retained in the lungs)
  • 24. Volcanic Ash / Dust / Sand Aerosols Volcanic Ash Cloud Volcanic Dust Contamination Sand Aerosol Contamination Visibility Clearly visible from all angles, easily identifiable by dark colour, distinct boundary Visible only from selected angles, hard to distinguish, visible in satellite imagery Visible sometimes from selected angles, visible in satellite imagery Where? Within 1-200 NM of the eruption up to 500 NM Very large areas (>1000 NM in size) Large areas Typical Concentrations (1 kg/hm3 = 10โˆ’3 g/m3 ) 1000 kg/hm3 1-100 kg/hm3 1-100 kg/hm3 Particle size range (ยตm) 1-2000 1-40 1-50 Floatability in atmosphere (age) 12 Hours (due to ash- dust differentiated sedimentation) 6 Days (traces remain for years) 3 Days 24
  • 25. Volcanic Ash Cloud Volcanic Dust Contamination Sand Aerosol Contamination Aviation Safety Risk Serious incidents, no injury accidents None on record None Impact on aviation Local Global due to misinterpretation Maintenance issues Source: Prof. Ulrich Schumann, DLR Institute of Atmospheric Physics, NASA Earth Observatory 25
  • 27. 16/02/2007 = 14 aircraft: windshield failures within 3ยฝh 19/01/2011 = 3 aircraft: windshield failures within ยฝh 27 Ash-Sized Sand โ€“ a New Safety Concern (Denver, CO) Source for photos: www.airliners.net Skywest Canadair CRJ-700 on behalf of United Airlines, flight OO-6761/UA-6761 from Denver, CO to Cleveland, OH (USA), reported a cracked windshield during initial climb out of runway 34R and returned to Denver . Skywest Canadair CRJ-200 on behalf of United Airlines, registration N978SW performing flight OO-6576/UA-6576 from Denver, CO (USA) to Winnipeg, MB (Canada), reported a windshield cracked during initial climb out of runway 34L and returned to Denver Delta Airlines Boeing 757-200, flight DL-1916 from Denver, CO to Atlanta, GA (USA), during initial climb out of runway 34L reported a cracked windshield and returned to Denver
  • 28. 28 Future Eruption First Reaction Checklist ๏ƒผ Location of the eruption / time: LAT, LONG, HHMMz, DDMMYY {repeat until eruption ends} ๏ƒผ How tall is the eruption column? ECH (m AMSL) ๏ƒผ Download wind profile in the area (e.g. from NOAA): WD/WV ๏ƒผ Calculate how far will the volcanic ash cloud go: VAMAX ๏ƒผ Draw a contour with VAMAX as major axis on the map: DA Ash4D
  • 29. 29 Volcanic Ash Danger Area Shape: defined by the variability of wind direction and amplitude of wind velocity
  • 30. 30 Volcanic Ash Danger Area How far does the VA travel? Function of: H (height of eruption column), FL (flight level), and WV (wind velocity) Eruption column H (m) 30000 Flight Level (100 ft) 100 Wind Velocity (kts) 50 Danger area (NM) 535 Pinatubo 1991 Eruption column H (m) 9000 Flight Level (100 ft) 100 Wind Velocity (kts) 100 Danger area (NM) 236 Eyjafjalla 2010 Eruption column H (m) 3500 Flight Level (100 ft) 30 Wind Velocity (kts) 20 Danger area (NM) 21 Etna 2011
  • 31. 31 Why 500 NM for Pinatubo = 250 NM for Eyjafjalla? Slide from Jacques Renvier, CFM/SNECMA, Atlantic Conference on Eyjafjallajokull, Keflavik 2010
  • 32. 32 Why 500 NM for Pinatubo = 250 NM for Eyjafjalla? (Kilauea, Hawaii 28 years continuous eruption)
  • 33. 33 Conclusions on Human Health Effects What was studied: passengers (short-term) and crew (long- term) exposure to volcanic dust concentrations of 4โˆ™10โ”€3 g/m3 โ€œWell under limits for short time exposure and even lower than those for chronic exposureโ€ โ€œReasonable to anticipate no risk for silicosis or lung cancer in passengers and crew membersโ€ โ€œConcentration lower than environmental Silica aerosols in some parts of the world (e.g. Ryadh, Cairo)โ€
  • 34. 34 Concentration: volatile, noisy, measured indirectly Direct and consistent methods to measure concentration in real time: none Indirect methods, subject to large methodical errors and measuring historical values of concentration along a line of sight/movement: โ€ข In-situ sampling; โ€ข Ground up-looking LIDAR; โ€ข Airborne down-looking LIDAR; โ€ข Ground optical photometre; โ€ข Satellite infrared image.
  • 35. 35 Concentration measurement problems: 1. scale of phenomenon and 2. consistency All these technologies deployed in the same area would yield different results
  • 36. 36 Hectometric Principle: Why do concentration measurements require averaging at the 1 hm3 scale? In this example we assume we want to measure the brightness of a halftone image
  • 37. 37 Future sensors are shortsighted and the scale of the phenomenon is larger
  • 38. 38 Types of concentrations Actual Measured Forecasted Blindly (open- loop) Forecasted with Data Assimilation When they are available (hours) never T+2H Tโˆ’18H (up to Tโˆ’180H) Tโˆ’18H (up to Tโˆ’180H) Uncertainty due to initial data of the eruption (orders of magnitude) - - 2 - 3 0.2 - 1 Uncertainty due to the Eulerian diffusion model (orders of magnitude) - - +1 every 24 hours 0.1 - 0.4 Uncertainty due to the measurement techniques - 0.1 โ€“ 1 - - Area coverage - Very local1 Global Global Overall errors 0 Significant Very large and rapidly increasing in time Large Relevance to IFR flight operations - Tactical avoidance Flight planning Flight planning Relevance to ATM - Forecasts Validation Airspace management, Flow management Airspace management, Flow management [1] Except the satellite images, which provide a global view
  • 39. Airborne in situ hectometric concentrationโ€ measurement unit isokinetic 39
  • 40. VADHCMU Volcanic Ash/Dust Hectometric Concentration Measurement Unit 1. Airborne 6 channel (3 wavelengths plus polarizations) backscattering infrared LIDAR, 2. Ground based (mobile) optical photometre, and 3. Airborne inโ€situ hectometric concentration measurement unit. A consistent and systematic measurement technology for data assimilation: 40
  • 41. 41 Selected Conclusions โ€ข Extending the term of volcanic ash cloud as per ICAO Doc9691 to the volcanic dust haze is wrong and misleading; โ€ข Size of the particles matters more than concentration as impact on aircraft and aircraft turbofan engines; โ€ข Predicting concentrations using a dispersion model with data assimilation from a systematic daily measurement scheme using hectometric in-situ samplers is the best choice for a way forward; โ€ข Immediate reaction to a VA threat should be based on a simple kinematic model of the extension of the volcanic ash cloud and not on chasing the dust going round the globe. Please, read the final report for more!

Editor's Notes

  1. Eurocontrol, University Politehnica of Bucharest, and Romatsa present the results of the volcanic ash safety research project, run between July 2010 and January 2011. At the Eurocontrol Safety Team of 22-23 June 2011, it was agreed to present these results to the International Volcanic Ash Task Force in Montreal, 11-15 July 2011.
  2. The study is the result of 7 months of research by a multidisciplinary team from the University Politehnica of Bucharest, Romania, Research Centre for Aeronautics and Space. The team was coordinated by Professor Octavian Thor Pleter.
  3. Codenamed โ€œAsh Safetyโ€, the study was delivered to the main beneficiary Eurocontrol in January 2011. The Romanian Air Traffic Services Administration (ROMATSA) is also involved in the next phases of the project.
  4. This presentation introduces the key results of the Ash Safety research in the following order: 1. Introduction โ€“ research subject, objectives, and relevance 2. Risks, vulnerability, and the scale of the phenomenon 3. Ash vs. Dust; sand aerosols; why does particle size matter? 4. Extent of the danger area: volcanic ash cloud estimation 5. Human health effects 6. Concentration measurement and forecasting and 7. Selected conclusions
  5. Eyjafjalla eruption in April and May 2010 created an unprecedented disruption of air traffic and the demand for objective, relevant, and scientifically validated information for the future decisions on the air traffic in volcanic ash contaminated atmosphere, for the best trade-off for the most fluent air traffic under the circumstances, with uncompromised flight safety. Under the circumstances, a research project โ€œon the Measurement and the Effects of the Volcanic Origin Particles in Suspension in the Atmosphere on the Safety of Aircraftโ€ seemed useful.
  6. The research report is easy to read, because it was written for aviation specialists, and not for researchers. Among major findings, the report confirms that the volcanic ash clouds are dangerous to aviation, as stated in the ICAO Doc9691. A cloud means a clearly visible undissipated matter, with a clear boundary. The safety risk of flying into such clouds is significant, regardless of concentration. However, extending this conclusion to volcanic dust contaminated areas is reported as wrong and misleading. Volcanic ash clouds are present in the vicinity of the volcano, and along a line down the wind, but they do not survive very long. In a couple of hours the volcanic ash particles sediment on the ground, and the remaining dust is much less worrying. The study explains why tactical avoidance of the volcanic dust contamination areas based on on-board instruments is not practical.
  7. The study has an important section dedicated to the impact of the volcanic ash/dust on the human respiratory system. No health risks were found for the occupants of an aircraft exposed to ash or dust contamination. Measuring ash concentration is not as easy as the aviation community expects. The study considered a wide range of measurement techniques, and the behaviour of this variable. An important conclusion is the scale of the phenomenon. Although concentration is measured in grams per cubic metre, it should be averaged at the order of a cubic hectometre, which equals one million cubic metres. This is called the hectometric principle. The authors advance an alternative format of the unit: kilograms per cubic hectometre. One kilogram per cubic hectometre is equivalent to ten to minus three grams per cubic metre, but is more suggestive as to the scale of the phenomenon.
  8. Concentration is seen as the key variable of the volcanic ash/dust contamination, and yet the study applied tribology research results and concluded that particle size is another variable, sometimes even more important. Ash and dust impact aircraft very differently at the same concentration, in both the abrasion effect and the glassy coating effect inside the turbine engines. The study advances a quick algorithm to assess the danger area in case of a new eruption, and the method to predict the contaminated areas with better accuracy.
  9. This table summarises all known outcomes of a volcanic ash encounter. Combustor deposits of melted ash, also known as โ€žglassy coatingโ€, could cause the turbine engines to surge or shut-down. Clogging the turbine cooling vents is another problem, which could result in engine overheating. The glass deposits on the high pressure turbine blades modify the flow of air and spoils the dynamic balance of the rotor, causing vibrations. And yet, not all these known effects are equally relevant to safety. Most of them concern maintenance.
  10. In order to rank the effects with respect to their impact on safety, we found that vulnerability is proportional to the order of magnitude of the air breathing. By far, the most vulnerable part of an aircraft is the turbine engine, because the order of magnitude is one thousand cubic metres per second. Other parts of the aircraft are exposed to ten times less intense airflow: windshield, empennage, body and wing. The human occupants, pitot-static sensors, computers, electrical engines and other air-cooled parts might be affected by a non-filtred airflow of an order of magnitude of zero point zero one cubic metres per second. Although not critical in terms of air breathing, the health of the aircraft occupants is a particularly sensitive issue, and it was addressed separately. The study shows that piston engines or air-cooled parts with air filters are not significantly affected by the volcanic particles.
  11. The critical vulnerability is that of the turbine engines. The quantity of air the turbine engines are ingesting is very high, and if the air is contaminated, this results in the exposure to a large quantity of contaminant. The silica particles in the core flow may be deposited as glass in the combustion chamber and on the high pressure turbine blades, as depicted in the image by the large orange dots. The safety troubles are very probable when the deposits amount to one kilogram per engine. Engine shut down and/or overheating are likely. However, restarting the engines has been always possible after exiting the contaminated area and after descent to 10,000 ft.
  12. The safety risk of flying into volcanic ash/dust contaminated atmosphere may be analysed using a characteristic time scope of 10 minutes. For an unexpected encounter with volcanic ash, 10 minutes would be the maximum time of exposure, provided the evasive manoeuvres are taken, as recommended by ICAO Doc9691. For expected encounters with low concentration volcanic dust, the duration of exposure expressed in units of 10 minutes of flight also makes sense. The volume of air ingested in a typical turbofan engine in this characteristic time of 10 minutes is of the order of one million cubic metres, or one cubic hectometre.
  13. To illustrate the air breathing vulnerability model, here is the quantity of contaminant accumulated in 10 minutes of flight in a concentration of two times ten to minus three grams per cubic metre, or two kilograms per cubic hectometre. Obviously, there is a major discrepancy in the impact on the aircraft hardware and liveware. Although just a fraction of the one point two kilograms of volcanic ash/dust is retained in the engines, in theory this quantity could be enough to upset their functionality.
  14. The study concludes that in terms of the impact on aircraft, it is worth discriminating on size, between volcanic ash and volcanic dust. Volcanic ash consists of particles between one sixteenth of a millimetre (sixty two point five microns) and two millimetres, whereas particles below that form the volcanic dust, also known as fine ash. Initially, the eruption column is a mixture of ash and dust. As they get carried by the aloft winds, the size distribution changes. The ash sediments typically within two hundred nautical miles, whereas the dust continues to float and to travel around the globe. Sedimentation of the ash particles is represented by the black dots that reach the ground level. The table contrasts the two particle types. The larger particles sediment close to the volcano, within hours from the eruption. An average time for a 1 mm particle could be around half an hour, while smaller dust particles may either sediment much later or not sediment at all, keeping afloat in the atmosphere for years.
  15. The picture shows a microscopic view of a sample of volcanic matter gathered in Iceland in April 2010. The two types of particles can be observed: dust particles as pointed by the white arrows and ash particles as shown by the blue ones. Although the number of the dust particles is very large compared to the ash particles, in quantitative terms, the dust is just a small fraction of the volcanic tephra.
  16. This discrimination between ash and dust is also relevant to the visibility of a so called โ€œcloudโ€. The volcanic ash cloud has a clear boundary and is clearly visible from all angles, whereas the volcanic dust forms a haze, only visible from selected angles, if at all visible. The volcanic dust are dissipated aerosols, also visible in the satellite images. Before April 2010 Eyjafjalla eruption, the safety concern regarded the volcanic ash cloud, which is a visible formation of undissipated matter. Our study does not endorse extending the safety concerns over to the volcanic dust haze. There is no rationale in equating volcanic ash clouds and volcanic dust haze.
  17. Let us consider the case of an eruption with a ten kilometres high column, and a steady wind of fifty knots. The table represents the falling speed in metres per second for two sizes of volcanic ash particles (one millimetre and one hundred microns) and for two sizes of volcanic dust particles (ten microns and one micron). The falling speed is decreasing with altitude, but considering an average falling speed is a fair approximation. Thus, our problem becomes linear. Of course, this is a major simplification from the movement calculated with the Eulerian and Lagrangian dispersion models that we have used in our study, but the approximation facilitates an intuitive approach. Visible ash clouds are threatening, but rather short-term and local. Volcanic dust contamination is a long-term and wide area issue, but its relevance to safety is less clear. Our conclusions are that it is relevant to maintenance rather than safety.
  18. The table and the diagram illustrate what happens with a ten kilometres high eruption in a fifty knots wind. Four types of particles are analysed: one millimetre and one hundred microns ash particles, and ten microns and one micron dust. Sedimentation time is huge for the dust, which could wander around the globe for almost forty thousand hours, covering close to two million nautical miles. If aviation would need to avoid flying into volcanic dust, this would ground it for good. It makes sense though to avoid flying into volcanic ash particles. They settle in two hundred nautical miles in this example, in four hours.
  19. Although experiments with turbine engines are too expensive, simulated experiments or results borrowed from sand blasting research conclude that the particle size is a key factor as to the abrasion effects. Here, the abrasion effect decreases as the size of the particles goes down from eight hundred to three hundred microns. Imagine that a stone hits your car windscreen and cracks it. Now imagine that you mill the stone, smashing of into particles of the size of dust. Although the quantity if the matter is the same, the dust particles will not harm your car. This happens regardless of concentration (either if the dust particles arrive in a tight formation, or one by one).
  20. The explanation is to be found in the ratio between the inertial forces and the aerodynamic forces. The drawing contrasts the movement of a volcanic ash particle and a volcanic dust particle around a wing profile. The dust follows the streamlines and avoids impacting the wing, so the abrasion is nil. Even if some of the dust particles will end up hitting the leading edge though, this will be a low percentage of the total number of particles, and in terms of quantity insignificant. Ash particles however are less capable of quick turns in the flow of air, and most of them will collide with the leading edge.
  21. The same analysis applies inside the core flow of a turbine engine. Both ash and dust particles are melted in the combustion chamber, and turn into liquid drops. However, in order to deposit as glassy coating, the drop has to come in contact to a colder surface, such as a turbine blade. This does not happen for the volcanic dust droplets, which are too small to impact surfaces. They exit the engine and solidify outside. The volcanic ash drops however are too heavy to follow the streamlines exactly, hitting the colder walls and clogging the engine.
  22. This represents the relative safety risk with respect to the size of the particles, as a cumulative effect of abrasion and glassy coating (turbine engine risk). Again, the relevant particle sizes are the volcanic ash particles.
  23. In the dust segment, the most safety-critical subsegment is one to ten microns. By coincidence, this is the case for both turbofan engines and the human respiratory system. Although we do not consider flying into volcanic dust as safety-critical, we analysed the sustainability of the flight in such conditions. The fan acts like a centrifugal separator, and particles above ten microns tend to bypass the combustion chamber.
  24. Making a comparison between volcanic ash, volcanic dust and sand aerosols contamination, the following conclusions can be drawn: Volcanic ash clouds are clearly visible from all angles, they are easily identifiable as they have a dark colour and clear contour. The opposite can be said about the volcanic dust and sand aerosols, which cannot be seen unless from selected angles, they are hard to distinguish and are generally visible in satellite imagery. Talking about the location where these types of matter can be found, volcanic ash usually gets as far as 200 NM, and in rare cases even 500 NM away. Volcanic dust behaves differently and may travel very large distances, more than 1000 NM. As for sand aerosol contamination, this can be found in the proximity of large areas covered with sand or at larger distances. Particle floatability in the atmosphere is smaller for the larger ash particles than for dust and sand aerosols. Ash may generally travel for maximum half a day, while dust and sand aerosols may float around for 3 and up to 6 days. Sometimes, dust traces may remain in the atmosphere for years.
  25. Regarding the aviation safety risk and the impact of volcanic origin matter on aviation, the table on this slide summarizes the following results: Encounters with volcanic ash clouds have so far registered serious incidents, but no injury accidents, and have had local impact only. There have been no records made on volcanic dust contamination so far, but the impact of this kind of particles is at this point a global one due to misinterpretation. Sand aerosols contamination is not known to have had any real impact on aviation other than maintenance issues.
  26. Analysing the safety impact using the severity-frequency framework, the data gathered by the authors indicated low severity for volcanic ash encounters and zero severity for the volcanic dust encounter. Severity is the probability of an occurrence to turn into an accident or incident. Representing graphically the severity on the vertical axis and the frequency safety risk on the horizontal axis, several types of occurrences have been mapped: structural failure, which is rather rare but has a high severity index, clear air turbulence, moderately frequent and severe, bird strikes with some severity, and sand aerosol encounters, with zero severity. Putting volcanic ash encounters and dust contamination on this graph, the authors appreciate, based on experiments and estimated computations, that coming across an ash cloud could happen almost as frequently as coming across sand aerosols and this may be qualified as a low severity occurrence when compared to the others previously mentioned. Volcanic dust encounters are likely to occur at least as often as volcanic ash encounters but, due to the fact that dust travels around the world for longer periods of time, the frequency of occurrence might be anywhere larger than the one marked for the volcanic ash. However, as the study shows, the severity of these occurrences approaches zero, as dust has no proven significant impact on flying aircraft.
  27. As the sand aerosols are used for comparison in this study, it is interesting to point out that there have been recorded situations when ash-sized sand particles have caused incidents of much higher severity than that of volcanic dust encounters. All the incidents took place in Denver โ€“ Colorado, first in 2007 and later, in 2011, during winter. The gross sand spread on roads was lifted in the atmosphere by the surface wind, causing windshield failure for 14 aircraft in 2007, and for 3 aircraft in 2011, in a rapid succession. These incidents were caused by ash-sized particles of sand (over sixty three microns).
  28. The study advances a first reaction checklist in case of future volcanic eruptions. The basic input data are the following: location and time of the eruption, meaning latitude, longitude, date and time of day, height of the eruption column above sea level. The forecasted wind vector field in the area may be downloaded from a number of sources, for instance from the National Oceanic and Atmospheric Administration. The wind direction and velocity profile in the area is used as a transport speed, and depending on the flight level on target, a certain distance may be computed using a simple kinematic linear formula. This distance is the volcanic ash particles range. This process is repeated until the eruption ends.
  29. Based on the distance of the volcanic ash reach, we may draw a contour of a trapezoidal shape. The apex is defined by the variability of the wind direction and amplitude of wind velocity translates into the length.
  30. Determining the distance the volcanic ash covers before falling below the target flight level implies the calculation of a simple linear formula based on the following parameters: height of the eruption column, flight level and wind velocity. This could then provide input for defining a volcanic ash danger area. Three examples of eruptions and their parameters illustrate this simple, linear approximation.
  31. This slide belongs to Jacques Renvier, from CFM/SNECMA, and illustrates the known occurrences placed on a distance from volcano โ€“ flight level diagram. The green dots represent benign encounters, the orange diamonds stand for slight damage without immediate operational effects and the red squares represent high severity encounters: in-flight shut downs. The conclusion from the diagram is that there are no immediate operational issues at a distance above one thousand kilometres or five hundred and forty miles from the volcano. We agree, and moreover, this limit corresponds to a special eruption: Pinatubo 1991. In any other eruption, this limit is significantly lower. Why?
  32. Why five hundred miles for the Pinatubo 1991 eruption are equivalent to two hundred and fifty miles for the Eyjafjalla 2010 eruption? This simplified diagram explains why. The combination of the height of the eruption column and the velocity of the aloft wind causes the volcanic ash to cover larger or lower distances. Pinatubo eruption of 1991 had the highest eruption column in the known history, thirty kilometres above sea level. It would be a waste to calculate a one thousand kilometres safety distance based on that for an eruption such as Eyjafjalla 2010. The diagram shows that the Grimsvatn eruption of 2011 twenty kilometres in height has roughly the same distance of volcanic ash impact as Eyjafjalla due to the lower wind velocity. Calculations considered the one hundred microns ash particles, falling with an average rate of descent of zero point seven metres per second.
  33. Discussing the human health effects, the study covers the passengers short term and crew members long term exposure to volcanic dust concentrations of four times ten to minus three grams per cubic metre. The study concluded that this is well under limits for short time exposure and even lower for chronic exposure. Furthermore, it is reasonable to anticipate that there is no risk for silicosis or lung cancer in passengers and crew members. Also, the contaminant concentration proved to be lower than environmental Silica aerosols in some parts of the world (e.g. Ryadh, Cairo).
  34. A chapter of the study is dedicated to the classic measuring techniques for the concentration of the volcanic ash/dust particles: in-situ sampling, ground up-looking LIDAR, airborne down-looking LIDAR, ground optical photometre, and satellite infrared image. Contrary to what many people expect, there are no direct, accurate and reliable methods to measure concentration in 3D in real time. The indirect methods considered here determine the concentration along a line of sight or a line of movement. Apart from that, there is a number of calibration parameters and arbitrary assumptions, which challenge the consistency and in the end the practical relevance of the results. On top of that, current in-situ samplers do not observe the hectometric principle, and thus draw a random value out of the range of a noisy random variable.
  35. The scale of phenomenon problems and the consistency problems lead to large errors. The drawing illustrates measuring the concentration by various classical techniques deployed in the same area. The ground up-looking LIDAR and the airborne down-looking LIDAR follow a vertical line of sight and measure the concentration along a line of movement with the wind velocity and ground speed respectively. In-situ sampling devices integrate the concentration along a line of movement aligned to the airspeed. The ground photometer requires a line of sight towards the Sun. Finally, the satellites integrate concentration along a divergent family of lines of sight towards the Earth.
  36. This example illustrates what happens when a noisy variable such as concentration is not averaged at the scale of the phenomenon: the measurement results could be anywhere between zero and maximum, becoming irrelevant. A halftone grey with 30% brightness could be mistakenly measured as 0% (white) or 100% (black) when the measurement scope is not large enough. A solution for eliminating or reducing these errors is to average the measurements at the scale of the phenomenon. In the case of volcanic ash/dust concentration, this is one cubic hectometre, as explained earlier.
  37. Hope is growing that new concentration measuring devices will solve the problem of the tactical avoidance of the volcanic ash/dust contaminated areas. This way, these contaminated areas could be treated as thunderstorms or other weather phenomena. Our study shows that these new devices are short sighted, meaning that information is available only a few nautical miles ahead. For example, a LIDAR look-ahead distance is up to seven nautical miles, while the AVOID system developed by Dr. Fred Prata and easyJet is the best performer with fifty four nautical miles look ahead. The slide illustrates why tactical avoidance is a very long shot, even for the AVOID device. Whereas thunderstorm cells typical diameter is of the order of one hundred nautical miles, the look-ahead of an airborne weather radar is three hundred and twenty miles. The tactical avoidance capacity is given by this ratio: three hundred and twenty by one hundred. In the case of volcanic ash/dust contaminated areas, it is worse both ways: contamination cells are larger, and the look-aheads of the devices are smaller. An aircraft attempting tactical avoidance could be trapped as shown.
  38. This table is a synthesis of the four types of concentration information: actual values, measured values, predicted values without and with data assimilation. They are described in terms of availability, uncertainty, errors, and relevance to operators and air navigation service providers. Manufacturers would like to use actual values, which in the opinion of the authors of this study are a total utopia. Measured values have their problems already mentioned and are available too late for practical use. Open-loop or blind forecasts have raised credibility issues. However, the study concluded that the best type of information to use in the future would be the forecasted values with data assimilation from a systematic and consistent scheme of daily measurements, based on the hectometric principle.
  39. This is a cross section of an airborne inโ€situ hectometric concentration measurement unit advanced by the authors. It is an isokinetic air absorber hooked under the wing of an experimental aircraft. It accumulates a quantity of contaminant out of the ingested one cubic hectometre of air. Unlike other in-situ samplers, this is designed specifically to provide consistent measurements of the volcanic ash or dust concentration for aviation use.
  40. Measurements for data assimilation require special consistency and comparability. For that purpose, the study advances a so called Volcanic Ash/Dust Hectometric Concentration Measurement Unit, which consists of a standardized battery of the following devices deployed simultaneously, in the same area: an airborne 6 channel backscattering infrared LIDAR, a ground based (mobile) optical photometre, and an airborne inโ€situ hectometric concentration measurement unit as presented previously. Standardization of these batteries is important. Using measurement data from various sources, coming from a multitude of unstandardized devices could compromise the efforts. Similar error patterns may be filtered out by software, as opposed to the dissimilar error patterns. The measurements should be carried out on a daily basis in those areas where the added value of the data assimilation is best. The forecasting model could calculate where this area would be for the next day.
  41. There are many conclusions of this study, and these four seem the most important at this stage: 1. Extending the term of volcanic ash cloud as per ICAO Doc9691 to the volcanic dust haze is wrong and misleading. 2. Size of the particles matters more than concentration as impact on aircraft and aircraft turbofan engines. 3. Predicting concentrations using a dispersion model with data assimilation from a systematic daily measurement scheme using hectometric in-situ samplers is the best choice for a way forward. 4. Immediate reaction to a VA threat should be based on a simple kinematic model of the extension of the volcanic ash cloud and not on chasing the dust going round the globe. Please, read the report for more.