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PRIME2 Consequence Analysis
and Model Evaluation
Pacific Northwest International
Section of the A&WMA
2017 Annual Conference
Boise, ID.
Sergio A. Guerra, PhD
Ron Petersen, PhD, CCM
November 3, 20171
Outline
1. Background on PRIME2
2. Consequence Analysis
3. Field Evaluation
4. Case studies
2 PRIME2 Consequence Analysis and Model Evaluation
3
Key Features of PRIME2
• Building wake effects decay rapidly back to ambient levels above the
top of the building versus the current theory that has these effects
extending up to 3 building heights.
• Lateral dispersion enhancement in the wake is less than vertical
dispersion enhancement (current PRIME has them identical).
• The approach turbulence and wind speed is calculated at a more
appropriate height versus the current theory where half the wake
height at 15 building heights downwind of the building is used.
• Wake effects for streamlined structures are reduced.
• Wake effects decrease as approach roughness increases.
PRIME2 Consequence Analysis and Model Evaluation
4
Project Summary
• Wind tunnel testing was performed to evaluate downwash effects from
rectangular and streamlined structures.
• CPP developed equations for predicting wind speed and turbulence in
building wakes for rectangular and streamlined structures based on wind
tunnel observations.
• CPP’s updates were compiled into a new AERMOD executable (PRIME2).
• Field versus model comparisons show that PRIME2 predictions are
generally within a factor of two of field observations but have a
overprediction tendency. Predictions also tend to be higher values than
with PRIME.
• Other theoretical problems have been identified. Correcting these may
alleviate the current overprediction tendency in PRIME2.
PRIME2 Consequence Analysis and Model Evaluation
Implementation Process
CPP and ORD
Submittals to
EPA OAQPS
Journal
Articles
Published
OAQPS Codes
CPP and ORD
Enhancements
EPA releases
New PRIME
as Alpha
option
EPA
releases
PRIME as
Beta
option
Notice of
proposed
rulemaking
(NPRM)
New PRIME
is released
as default
regulatory
option
Alpha option needs to meet the alternative refined model requirements in App W, Section 3.2.2
before it can become a Beta option. These requirements include:
1-Model has received a scientific peer review;
2-Model can be demonstrated to be applicable to the problem on a theoretical basis;
3-The data bases to perform analysis are available and adequate;
4-Appropriate performance evaluations show model is not biased toward underestimation; and
5-A protocol on methods and procedures to be followed has been established
5 PRIME2 Consequence Analysis and Model Evaluation
Consequence Analysis
PRIME2 Consequence Analysis and Model Evaluation6
PRIME2 Consequence Analysis and Model Evaluation7
PRIME2_v17234a Evaluation
1:10:10 BDG with MakeMet Hs=1.2Hb
PRIME2_v17234a2
AERMOD_v16216r
zo=2cm zo=25cm zo=100cm
Max=173.0 ug/m3
Max=73.5 ug/m3
Max=132.9 ug/m3
Max=72.2 ug/m3 Max=79.0 ug/m3
Max=70.9 ug/m3
PRIME2 Consequence Analysis and Model Evaluation8
PRIME2_v17234a Evaluation
1:10:10 BDG with MakeMet Hs=1.5Hb
PRIME2_v17234a2
AERMOD_v16216r
zo=2cm zo=25cm zo=100cm
Max=130.1 ug/m3 Max=97.0 ug/m3 Max=53.2 ug/m3
Max=68.8 ug/m3 Max=69.1 ug/m3 Max=66.8 ug/m3
PRIME2 Consequence Analysis and Model Evaluation9
PRIME2_v17234a Evaluation
1:10:10 BDG with MakeMet Hs=2.5Hb
PRIME2_v17234a2
AERMOD_v16216r
zo=2cm zo=25cm zo=100cm
Max=37.2 ug/m3 Max=26.6 ug/m3 Max=23.1 ug/m3
Max=37.8 ug/m3 Max=35.6 ug/m3 Max=37.9 ug/m3
PRIME2 Consequence Analysis and Model Evaluation10
PRIME2_v17234a Evaluation
Bowline Point BDGs with Bowline Met Data
PRIME2_v17234a2
AERMOD_v16216r
Hs=1.33Hb=87.8m Hs=1.80Hb=117.4m Hs=2.50Hb=163.1m
Max=1013.1 ug/m3
Max=638.3 ug/m3 Max=279.9 ug/m3
Max=279.9 ug/m3
Max=192.2 ug/m3
Max=192.2 ug/m3
Max Observed = 823.5 ug/m3
Field Evaluation
PRIME2 Consequence Analysis and Model Evaluation11
Bowline Point Field Evaluation for Receptors 1 and 3
Q-Q Plot of Predicted vs. Observed Concs. with BPIP Values
Model Version
Top 25 Mean
X obs
Top 25 Mean
X predict
Top 25
Pre/Obs
Fractional
Bias
R1&3 AERMODv16216r (ug/m3) 422.17 447.71 1.06 0.06
R1&3 PRIME2v17234a (ug/m3) 422.17 684.51 1.62 0.47
PRIME2 Consequence Analysis and Model Evaluation12
Refined BPIP Method Example
Bowline Point
PRIME2 Consequence Analysis and Model Evaluation13
Refined BPIP Method Example: Bowline Point
Merged Tiers
Building
Dimensions
BPIP
(m)
Updated BPIP
(m)
Building Height(Hb) 65.23 65.23
Building Width (W) 121.95 121.95
Building Length (L) 109.93 35.98
XBADJ -127.62 -97.20
YBADJ -2.47 -2.5
Assumption 1:
Tallest tiers combine
(green bdg)
Assumption 2:
BDG WIDTH (W) is
crosswind width of
merged tier.
Assumption 3:
XBADJ starts at the
upwind edge of the
merged tier
Assumption 4:
BDG LENGTH (L) is
calculated by dividing
the area of the
merged tier by W
PRIME2 Consequence Analysis and Model Evaluation14
Refined BPIP Method Example: Bowline Point
Unmerged Tiers
Building
Dimensions
BPIP
(m)
Updated BPIP
(m)
Building Height(Hb) 65.23 65.23
Building Width (W) 94.57 49.9
Building Length (L) 130.27 27.65
XBADJ -132.56 -127.90
YBADJ -27.17 -4.0
Assumption 1:
Tallest tiers do not
combine (green bdg)
Assumption 2:
BDG WIDTH (W) is
crosswind width of
unmerged tier.
Assumption 3:
XBADJ starts at the
upwind edge of the
tallest tier
Assumption 4:
BDG LENGTH (L) is
calculated by dividing
the area of the tallest
tier by W
PRIME2 Consequence Analysis and Model Evaluation15
Bowline Point Field Evaluation for Receptors 1 and 3
Q-Q Plot of Predicted vs. Observed Concs. with BPIP Values
Model Version
Top 25 Mean
X obs
Top 25 Mean
X predict
Top 25
Pre/Obs
Fractional
Bias
R1&3 AERMODv16216r (ug/m3) 422.17 447.71 1.06 0.06
R1&3 PRIME2v17234a (ug/m3) 422.17 684.51 1.62 0.47
PRIME2 Consequence Analysis and Model Evaluation16
Model Version
Top 25 Mean
X obs
Top 25 Mean
X predict
Top 25
Pre/Obs
Fractional
Bias
R1&3 AERMODv16216r (ug/m3) 422.17 237.67 0.56 -0.56
R1&3 PRIME2v17234a (ug/m3) 422.17 535.01 1.27 0.24
Bowline Point Field Evaluation for Receptors 1 and 3
Q-Q Plot of Predicted vs. Observed Concs. with Modified BPIP Values
PRIME2 Consequence Analysis and Model Evaluation17
Refined BPIP Method Example
Alaska North Slope
PRIME2 Consequence Analysis and Model Evaluation18
Model Version
Top 25 Mean
X obs
Top 25 Mean
X predict
Top 25
Pre/Obs
Fractional Bias
AERMODv16216r 3.13 3.59 1.15 0.137
PRIME2_17234 3.13 7.58 2.42 0.829
Alaska North Slope Field Evaluation
Q-Q Plot of Predicted vs. Observed Concs. with BPIP Values
PRIME2 Consequence Analysis and Model Evaluation19
Building
Dimensions
BPIP
(m)
Updated BPIP
(m)
Building Height(Hb) 34.0 34.0
Building Width (W) 51.26 51.26
Building Length (L) 55.67 25.81
XBADJ -45.24 -43.70
YBADJ 6.58 6.6
Assumption 1:
Tallest tier combine
(green bdg)
Assumption 2:
BDG WIDTH (W) is
crosswind width of
merged tier.
Assumption 2:
XBADJ starts at the
lee edge of the
merged tier
Assumption 3:
YBADJ is calculated
by dividing the area
of the merged tier by
the width of the
artificially created
building
Refined BPIP Method Example: Alaska North Slope
Merged Tiers
PRIME2 Consequence Analysis and Model Evaluation20
Building
Dimensions
BPIP
(m)
Updated BPIP
(m)
Building Height(Hb) 34.0 34.0
Building Width (W) 52.98 20.25
Building Length (L) 28.61 25.30
XBADJ -28.7 -28.6
YBADJ -11.79 4.8
Assumption 1:
Tallest tier do not
combine (green bdg)
Assumption 2:
XBADJ starts at the
lee edge of the
merged tier
Assumption 3:
YBADJ is calculated
by dividing the area
of the merged tier by
the width of the
artificially created
building
Refined BPIP Method Example: Alaska North Slope
Unmerged Tiers
PRIME2 Consequence Analysis and Model Evaluation21
Model Version
Top 25 Mean
X obs
Top 25 Mean
X predict
Top 25
Pre/Obs
Fractional Bias
AERMODv16216r 3.13 3.59 1.15 0.137
PRIME2_17234 3.13 7.58 2.42 0.829
Alaska North Slope Field Evaluation
Q-Q Plot of Predicted vs. Observed Concs. with BPIP Values
PRIME2 Consequence Analysis and Model Evaluation22
Model Version
Top 25 Mean
X obs
Top 25 Mean
X predict
Top 25
Pre/Obs
Fractional Bias
AERMODv16216r 3.13 2.78 0.89 -0.120
PRIME2_17234 3.13 6.14 1.96 0.648
Alaska North Slope Field Evaluation
Q-Q Plot of Predicted vs. Observed Concs. with Modified BPIP Values
PRIME2 Consequence Analysis and Model Evaluation23
Alaska North Slope: Observed Values
Max: 5.29 µg/m3
PRIME2 Consequence Analysis and Model Evaluation24
Alaska North Slope: AERMODv16216r
Max: 4.48 µg/m3
PRIME2 Consequence Analysis and Model Evaluation25
Alaska North Slope: PRIME2v17234a
Max: 13.20 µg/m3
PRIME2 Consequence Analysis and Model Evaluation26
What Could be Causing Higher PRIME2 Predictions?
• BPIP Building Dimensions Inputs: Building length and upwind and
downwind faces not defined correctly.
• Streamlines: Need to be reviewed and updated as necessary.
• The wind speed used to calculate concentrations. Currently PRIME
and PRIME2 are using the stack height wind speed.
PRIME2 Consequence Analysis and Model Evaluation27
Case Study Comparison
PRIME2 Consequence Analysis and Model Evaluation28
BPIP Values: AERMODv16216r
H1H 24-hr avg = 78.9ug/m3
PRIME2 Consequence Analysis and Model Evaluation29
BPIP Values: PRIME2_17234a2
PRIME2 Consequence Analysis and Model Evaluation30
H1H 24-hr avg = 41.4ug/m3
EBD Values: AERMODv16216r
PRIME2 Consequence Analysis and Model Evaluation31
H1H 24-hr avg = 39.5ug/m3
Conclusions
• PRIME2 includes a superior theory to account for building
downwash effects for rectangular and streamlined structures.
• Benefits from improved theory cannot be fully realized due to
outstanding issues in the model.
• Work from EPA ORD complements the work performed by
CPP.
• Plan is to continue EPA collaboration to address model
improvements to AERMOD related to building downwash.
PRIME2 Consequence Analysis and Model Evaluation32
Sergio A. Guerra, PhD Ron Petersen, PhD, CCM
sguerra@cppwind.com rpetersen@cppwind.com
Mobile: + 612 584 9595 Mobile:+1 970 690 1344
wwww.SergioAGuerra.com
CPP, Inc.
2400 Midpoint Drive, Suite 190
Fort Collins, CO 80525
+ 970 221 3371
www.cppwind.com @CPPWindExperts
Questions?
33 PRIME2 Consequence Analysis and Model Evaluation

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PRIME2: Consequence Analysis and Model Evaluation

  • 1. PRIME2 Consequence Analysis and Model Evaluation Pacific Northwest International Section of the A&WMA 2017 Annual Conference Boise, ID. Sergio A. Guerra, PhD Ron Petersen, PhD, CCM November 3, 20171
  • 2. Outline 1. Background on PRIME2 2. Consequence Analysis 3. Field Evaluation 4. Case studies 2 PRIME2 Consequence Analysis and Model Evaluation
  • 3. 3 Key Features of PRIME2 • Building wake effects decay rapidly back to ambient levels above the top of the building versus the current theory that has these effects extending up to 3 building heights. • Lateral dispersion enhancement in the wake is less than vertical dispersion enhancement (current PRIME has them identical). • The approach turbulence and wind speed is calculated at a more appropriate height versus the current theory where half the wake height at 15 building heights downwind of the building is used. • Wake effects for streamlined structures are reduced. • Wake effects decrease as approach roughness increases. PRIME2 Consequence Analysis and Model Evaluation
  • 4. 4 Project Summary • Wind tunnel testing was performed to evaluate downwash effects from rectangular and streamlined structures. • CPP developed equations for predicting wind speed and turbulence in building wakes for rectangular and streamlined structures based on wind tunnel observations. • CPP’s updates were compiled into a new AERMOD executable (PRIME2). • Field versus model comparisons show that PRIME2 predictions are generally within a factor of two of field observations but have a overprediction tendency. Predictions also tend to be higher values than with PRIME. • Other theoretical problems have been identified. Correcting these may alleviate the current overprediction tendency in PRIME2. PRIME2 Consequence Analysis and Model Evaluation
  • 5. Implementation Process CPP and ORD Submittals to EPA OAQPS Journal Articles Published OAQPS Codes CPP and ORD Enhancements EPA releases New PRIME as Alpha option EPA releases PRIME as Beta option Notice of proposed rulemaking (NPRM) New PRIME is released as default regulatory option Alpha option needs to meet the alternative refined model requirements in App W, Section 3.2.2 before it can become a Beta option. These requirements include: 1-Model has received a scientific peer review; 2-Model can be demonstrated to be applicable to the problem on a theoretical basis; 3-The data bases to perform analysis are available and adequate; 4-Appropriate performance evaluations show model is not biased toward underestimation; and 5-A protocol on methods and procedures to be followed has been established 5 PRIME2 Consequence Analysis and Model Evaluation
  • 6. Consequence Analysis PRIME2 Consequence Analysis and Model Evaluation6
  • 7. PRIME2 Consequence Analysis and Model Evaluation7 PRIME2_v17234a Evaluation 1:10:10 BDG with MakeMet Hs=1.2Hb PRIME2_v17234a2 AERMOD_v16216r zo=2cm zo=25cm zo=100cm Max=173.0 ug/m3 Max=73.5 ug/m3 Max=132.9 ug/m3 Max=72.2 ug/m3 Max=79.0 ug/m3 Max=70.9 ug/m3
  • 8. PRIME2 Consequence Analysis and Model Evaluation8 PRIME2_v17234a Evaluation 1:10:10 BDG with MakeMet Hs=1.5Hb PRIME2_v17234a2 AERMOD_v16216r zo=2cm zo=25cm zo=100cm Max=130.1 ug/m3 Max=97.0 ug/m3 Max=53.2 ug/m3 Max=68.8 ug/m3 Max=69.1 ug/m3 Max=66.8 ug/m3
  • 9. PRIME2 Consequence Analysis and Model Evaluation9 PRIME2_v17234a Evaluation 1:10:10 BDG with MakeMet Hs=2.5Hb PRIME2_v17234a2 AERMOD_v16216r zo=2cm zo=25cm zo=100cm Max=37.2 ug/m3 Max=26.6 ug/m3 Max=23.1 ug/m3 Max=37.8 ug/m3 Max=35.6 ug/m3 Max=37.9 ug/m3
  • 10. PRIME2 Consequence Analysis and Model Evaluation10 PRIME2_v17234a Evaluation Bowline Point BDGs with Bowline Met Data PRIME2_v17234a2 AERMOD_v16216r Hs=1.33Hb=87.8m Hs=1.80Hb=117.4m Hs=2.50Hb=163.1m Max=1013.1 ug/m3 Max=638.3 ug/m3 Max=279.9 ug/m3 Max=279.9 ug/m3 Max=192.2 ug/m3 Max=192.2 ug/m3 Max Observed = 823.5 ug/m3
  • 11. Field Evaluation PRIME2 Consequence Analysis and Model Evaluation11
  • 12. Bowline Point Field Evaluation for Receptors 1 and 3 Q-Q Plot of Predicted vs. Observed Concs. with BPIP Values Model Version Top 25 Mean X obs Top 25 Mean X predict Top 25 Pre/Obs Fractional Bias R1&3 AERMODv16216r (ug/m3) 422.17 447.71 1.06 0.06 R1&3 PRIME2v17234a (ug/m3) 422.17 684.51 1.62 0.47 PRIME2 Consequence Analysis and Model Evaluation12
  • 13. Refined BPIP Method Example Bowline Point PRIME2 Consequence Analysis and Model Evaluation13
  • 14. Refined BPIP Method Example: Bowline Point Merged Tiers Building Dimensions BPIP (m) Updated BPIP (m) Building Height(Hb) 65.23 65.23 Building Width (W) 121.95 121.95 Building Length (L) 109.93 35.98 XBADJ -127.62 -97.20 YBADJ -2.47 -2.5 Assumption 1: Tallest tiers combine (green bdg) Assumption 2: BDG WIDTH (W) is crosswind width of merged tier. Assumption 3: XBADJ starts at the upwind edge of the merged tier Assumption 4: BDG LENGTH (L) is calculated by dividing the area of the merged tier by W PRIME2 Consequence Analysis and Model Evaluation14
  • 15. Refined BPIP Method Example: Bowline Point Unmerged Tiers Building Dimensions BPIP (m) Updated BPIP (m) Building Height(Hb) 65.23 65.23 Building Width (W) 94.57 49.9 Building Length (L) 130.27 27.65 XBADJ -132.56 -127.90 YBADJ -27.17 -4.0 Assumption 1: Tallest tiers do not combine (green bdg) Assumption 2: BDG WIDTH (W) is crosswind width of unmerged tier. Assumption 3: XBADJ starts at the upwind edge of the tallest tier Assumption 4: BDG LENGTH (L) is calculated by dividing the area of the tallest tier by W PRIME2 Consequence Analysis and Model Evaluation15
  • 16. Bowline Point Field Evaluation for Receptors 1 and 3 Q-Q Plot of Predicted vs. Observed Concs. with BPIP Values Model Version Top 25 Mean X obs Top 25 Mean X predict Top 25 Pre/Obs Fractional Bias R1&3 AERMODv16216r (ug/m3) 422.17 447.71 1.06 0.06 R1&3 PRIME2v17234a (ug/m3) 422.17 684.51 1.62 0.47 PRIME2 Consequence Analysis and Model Evaluation16
  • 17. Model Version Top 25 Mean X obs Top 25 Mean X predict Top 25 Pre/Obs Fractional Bias R1&3 AERMODv16216r (ug/m3) 422.17 237.67 0.56 -0.56 R1&3 PRIME2v17234a (ug/m3) 422.17 535.01 1.27 0.24 Bowline Point Field Evaluation for Receptors 1 and 3 Q-Q Plot of Predicted vs. Observed Concs. with Modified BPIP Values PRIME2 Consequence Analysis and Model Evaluation17
  • 18. Refined BPIP Method Example Alaska North Slope PRIME2 Consequence Analysis and Model Evaluation18
  • 19. Model Version Top 25 Mean X obs Top 25 Mean X predict Top 25 Pre/Obs Fractional Bias AERMODv16216r 3.13 3.59 1.15 0.137 PRIME2_17234 3.13 7.58 2.42 0.829 Alaska North Slope Field Evaluation Q-Q Plot of Predicted vs. Observed Concs. with BPIP Values PRIME2 Consequence Analysis and Model Evaluation19
  • 20. Building Dimensions BPIP (m) Updated BPIP (m) Building Height(Hb) 34.0 34.0 Building Width (W) 51.26 51.26 Building Length (L) 55.67 25.81 XBADJ -45.24 -43.70 YBADJ 6.58 6.6 Assumption 1: Tallest tier combine (green bdg) Assumption 2: BDG WIDTH (W) is crosswind width of merged tier. Assumption 2: XBADJ starts at the lee edge of the merged tier Assumption 3: YBADJ is calculated by dividing the area of the merged tier by the width of the artificially created building Refined BPIP Method Example: Alaska North Slope Merged Tiers PRIME2 Consequence Analysis and Model Evaluation20
  • 21. Building Dimensions BPIP (m) Updated BPIP (m) Building Height(Hb) 34.0 34.0 Building Width (W) 52.98 20.25 Building Length (L) 28.61 25.30 XBADJ -28.7 -28.6 YBADJ -11.79 4.8 Assumption 1: Tallest tier do not combine (green bdg) Assumption 2: XBADJ starts at the lee edge of the merged tier Assumption 3: YBADJ is calculated by dividing the area of the merged tier by the width of the artificially created building Refined BPIP Method Example: Alaska North Slope Unmerged Tiers PRIME2 Consequence Analysis and Model Evaluation21
  • 22. Model Version Top 25 Mean X obs Top 25 Mean X predict Top 25 Pre/Obs Fractional Bias AERMODv16216r 3.13 3.59 1.15 0.137 PRIME2_17234 3.13 7.58 2.42 0.829 Alaska North Slope Field Evaluation Q-Q Plot of Predicted vs. Observed Concs. with BPIP Values PRIME2 Consequence Analysis and Model Evaluation22
  • 23. Model Version Top 25 Mean X obs Top 25 Mean X predict Top 25 Pre/Obs Fractional Bias AERMODv16216r 3.13 2.78 0.89 -0.120 PRIME2_17234 3.13 6.14 1.96 0.648 Alaska North Slope Field Evaluation Q-Q Plot of Predicted vs. Observed Concs. with Modified BPIP Values PRIME2 Consequence Analysis and Model Evaluation23
  • 24. Alaska North Slope: Observed Values Max: 5.29 µg/m3 PRIME2 Consequence Analysis and Model Evaluation24
  • 25. Alaska North Slope: AERMODv16216r Max: 4.48 µg/m3 PRIME2 Consequence Analysis and Model Evaluation25
  • 26. Alaska North Slope: PRIME2v17234a Max: 13.20 µg/m3 PRIME2 Consequence Analysis and Model Evaluation26
  • 27. What Could be Causing Higher PRIME2 Predictions? • BPIP Building Dimensions Inputs: Building length and upwind and downwind faces not defined correctly. • Streamlines: Need to be reviewed and updated as necessary. • The wind speed used to calculate concentrations. Currently PRIME and PRIME2 are using the stack height wind speed. PRIME2 Consequence Analysis and Model Evaluation27
  • 28. Case Study Comparison PRIME2 Consequence Analysis and Model Evaluation28
  • 29. BPIP Values: AERMODv16216r H1H 24-hr avg = 78.9ug/m3 PRIME2 Consequence Analysis and Model Evaluation29
  • 30. BPIP Values: PRIME2_17234a2 PRIME2 Consequence Analysis and Model Evaluation30 H1H 24-hr avg = 41.4ug/m3
  • 31. EBD Values: AERMODv16216r PRIME2 Consequence Analysis and Model Evaluation31 H1H 24-hr avg = 39.5ug/m3
  • 32. Conclusions • PRIME2 includes a superior theory to account for building downwash effects for rectangular and streamlined structures. • Benefits from improved theory cannot be fully realized due to outstanding issues in the model. • Work from EPA ORD complements the work performed by CPP. • Plan is to continue EPA collaboration to address model improvements to AERMOD related to building downwash. PRIME2 Consequence Analysis and Model Evaluation32
  • 33. Sergio A. Guerra, PhD Ron Petersen, PhD, CCM sguerra@cppwind.com rpetersen@cppwind.com Mobile: + 612 584 9595 Mobile:+1 970 690 1344 wwww.SergioAGuerra.com CPP, Inc. 2400 Midpoint Drive, Suite 190 Fort Collins, CO 80525 + 970 221 3371 www.cppwind.com @CPPWindExperts Questions? 33 PRIME2 Consequence Analysis and Model Evaluation