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                           Paper submitted for the Proceedings of the 
               2nd International Symposium on Freeway and Tollway Operations 
                              Honolulu, Hawaii – June 21‐24, 2009 
 
 
Irregularities  in  the  output  of  transport  planning  models’  forecasts  for 
capital infrastructure planning decisions 
 
C. Antoniou1, B. Psarianos1, and W. Brilon2 
 
                                           Abstract 
 
In  this  paper,  evidence  from  the  literature  on  the  inaccuracy  of  forecasts  from 
transport planning models is presented and its impact on capital infrastructure 
planning  decision‐making  is  demonstrated.  Empirical  evidence  suggests  that 
forecasts  used  for  major  planning  decisions  internationally  have  been  found  to 
be rather inaccurate (when comparing forecast flows with actually realized flows 
after  time  passed).  Evidence  of  these  irregularities  in  the  case  of  a  major 
expressway  infrastructure  project  in  Southern  Greece  is  presented,  providing  a 
typical example of a country with an inadequate freeway network. Data from the 
immediate  impact  zone  of  the  Attiki  Odos  tollway  in  the  metropolitan  area  of 
Athens  are  used  to  demonstrate  that  the  project  resulted  in  a  considerable 
change  in  the  land  use  patterns  and  density,  resulting  in  the  generation  of 
additional traffic flows. Having demonstrated the need for re‐thinking how long‐
term  traffic  is  forecast,  suitable  recommendations  for  promising  directions  are 
made. Dealing with uncertainty is one key aspect that can be easily incorporated 
to existing forecasting tools. Furthermore, the need for more detailed and area‐
specific models, e.g. through the integration of activity‐based modeling, specific 
mobility patterns and demands etc. are also outlined. 
 

1. Introduction 
Transportation planning and forecasting models are used as the basis for capital 
infrastructure decisions. Quite often, however, the results of these models show 
considerable  irregularities,  when  compared  with  the  actual  traffic  observed 
when the forecast horizon has passed. This does not imply that the models or the 
modelers  underperformed,  but  rather  that  there  are  some  inherent  difficulties 
that  may  not  be  always  taken  into  account.  The  objective  of  this  paper  is  to 
provide  some  insight  into  these  difficulties,  through  a  review  of  related 
literature, and then attempt to quantify the impact of one such factor (the land‐
use – transport interaction) through an application in the Attiki Odos motorway 
in the Athens, Greece, area. 
                                                        
1  Laboratory  of  Transportation  Engineering,  National  Technical  University  of  Athens,  9  Heroon 

Polytechniou, GR‐15780 Athens, Greece 
Tel: +30 210 7722783, fax: +30 210 7722629, email: antoniou@central.ntua.gr (C. Antoniou)  
Tel: +30 210 7722628, fax: +30 210 7722629, email: bpsarian@mail.ntua.gr (B. Psarianos)  
2 Lehrstuhl für Verkehrswesen, Ruhr‐Universität Bochum, D ‐ 44780 Bochum, Germany 

Tel. +49 (0)234 322 5936, Fax: + 49 (0)234 32 14 151, e­mail: verkehrswesen@rub.de 


                                                                                               page. 1
 
 
According  to  Rodier  (2004),  it  is  widely  acknowledged  that  forecasts  produced 
by  travel  and  emission  models  are  typically  inaccurate;  it  is  not  uncommon  to 
find  large  differences  between  predicted  and  actual  outcomes.  Some 
transportation  professionals  believe  that  current  state‐of‐the‐art  methods  can 
forecast  emissions  with  an  accuracy  of  plus  or  minus  15  percent  to  30  percent 
(Chatterjee  et  al,  1997).  Rodier  (2004)  also  concludes  that  recent  evidence  for 
the induced travel hypothesis has increased concerns over the limited ability of 
most  regional  travel  demand  models  to  represent  how  an  increase  in  roadway 
supply reduces the time cost of travel and, to the extent that demand is elastic, 
increases the quantity of travel demanded.  
 
Parthasarathi and Levinson (2009) note that while research efforts have focused 
on improving the technical aspects of a typical four‐step transportation planning 
model, few studies have evaluated the model accuracy by comparing forecasts to 
actual  traffic  counts.  The  analysis  indicated  that  traffic  forecasts  on  61.5%  of 
the  links  were  underestimated  compared  to  the  actual  traffic  counts  and  the 
forecasts  were  more  accurate  for  higher  volume  roadways.  Parthasarathi  and 
Levinson (2009) also evaluate the accuracy of demand forecasts using a sample 
of  recently  completed  projects  in  Minnesota  (with  a  horizon  forecast  year  of 
2010 or earlier) and identify the factors influencing the inaccuracy in forecasts. 
The analysis indicates a general trend of underestimation in roadway traffic 
forecasts with factors such as highway type and functional classification playing 
an  influencing  role.  Roadways  with  higher  volumes  and  higher  functional 
classifications such as freeways are subject to more severe underestimation 
compared to lower volume roadways/functional classifications. 
 
An  explanation  for  the  underestimation  seen  in  forecasts,  specifically  road 
forecasts,  can  be  attributed  to  the  non­incorporation  of  induced  traffic  into 
the  model  forecasting  procedure  (Noland,  2001).  The  theory  of  induced 
demand  states  that  increases  in  highway  capacity  induces  additional  growth  in 
traffic  resulting  in  increased  levels  of  vehicle  traffic.  From  an  economic 
perspective,  the  travel  demand  increases  as  the  cost  of  travel  decreases  due  to 
capacity  improvements  resulting  in  an  elasticity  of  demand  associated  with 
travel (Noland and Lem, 2000).  
 
Flyvberg et al. (2006) present results from a large‐scale study of traffic forecasts 
in transportation infrastructure projects, using a sample covering 210 projects in 
14  nations  worth  US$58  billion.  The  study  shows  that  forecasters  generally 
do  a  poor  job  of  estimating  the  demand  for  transportation  infrastructure 
projects.  For  72%  of  rail  projects,  forecasts  are  overestimated  by  more  than 
two‐thirds.  For  50%  of  road  projects,  the  difference  between  actual  and 
forecasted  traffic  is  more  than  ±20%;  for  25%  of  road  projects,  the 
difference is larger than ±40%.  
 
 
 



                                                                                   page. 2
2. Factors affecting inaccuracy of transportation forecasting 
 
Sammer  (2006)  observes  that  while  the  currently  available  modelling 
approaches are considerably more flexible and powerful than those of the 1990s, 
there  is  considerable  evidence  that  the  gap  between  state­of­the­art  theory 
and  practice,  i.e.  the  actual  modelling  of  transport,  is  widening.  One  of  the 
implications of this observation is that trust in the validity of modelling results is 
decreasing  significantly.  Concluding,  Sammer  (2006)  summarizes  the  problems 
in  transportation  forecasting  as:  (i)  the  models,  and  especially  the  produced 
forecasts,  suffer  from  the  “black­box  effect”,  as  they  cannot  be  followed 
through and understood, (ii) many of the models are no longer state‐of‐the‐art, 
(iii)  there  is  little  or  no  evidence  for  the  validity  of  the  input  data  used  or 
how  the  model  was  calibrated,  and  (iv)  the  results  are  presented  as  point 
estimates,  rather  than  interval  estimates  based  on  a  probability  function,  with 
confidence limits specified.   
 
Transport models are (often complex) approximations of very complex systems. 
Therefore,  a  number  of  errors  can  occur  which  may  have  an  impact  on  the 
accuracy of the forecast results (Sammer, 2006): 
• Measurement errors; 
• Random errors; 
• Forecast errors due to the input data used; 
• Computational and application errors; 
• Model specification errors; 
• Transferability  errors  (when  attempting  to  apply  a  model  calibrated  in  one 
     region to another) 
• Aggregation and disaggregation errors. 
These  errors  may  either  result  in  additive  (or  even  multiplicative)  effects,  or 
cancel out (thus hiding potentially important model shortcomings).    
 
Litman (2005) examines how various land use factors such as density, regional 
accessibility, mix and roadway connectivity affect travel behaviour, including per 
capita  vehicle  travel,  mode  split  and  non‐motorized  travel.  Litman  concludes 
that  land  use  factors  can  have  significant  impacts  on  travel  patterns,  but 
that  current  transportation  models  are  not  accurate  at  predicting  their 
effects.  
 
Wegener  and  Fuerst  (1999)  indicate  that  the  impacts  of  transport  policies  on 
transport  patterns  are  clearer  and  stronger  compared  to  the  interplay  of  land 
use  and  transport.  While  travel  cost  and  travel  time  have  a  negative  impact  on 
both trip length and trip frequency, accessibility has a positive impact on trip 
length  and  frequency.  Mode  choice  is  dependent  upon  the  relative 
attractiveness of a mode compared to all other modes. The fastest and cheapest 
mode  is  likely  to  have  the  highest  modal  share.  In  general,  the  theoretical 
considerations support the conclusion that the impact of 'pull' measures, i.e. land 
use measures, is much weaker than the impact of 'push' measures, i.e. increases 
in travel time, travel cost etc.  
 



                                                                                      page. 3
3. An empirical analysis of the changes in land-use and traffic patterns
due to the Attiki Odos Motorway

In  this  section,  an  empirical  analysis  of  the  impact  of  land‐use  into  traffic 
patterns due to the Attiki Odos motorway in the Athens area is presented.  

3.1. Methodology for on‐site surveys for data‐collection 
One of the big challenges associated with modeling and other estimation efforts 
lies  in  the  original  data  input.  In  this  case,  we  have  relied  in  a  wide  variety  of 
sources  for  data  collection.  In  the  core  of  this  effort,  however,  is  a  set  of 
coordinated  on­site  surveys,  aimed  at  providing  first‐hand,  reliable  evidence 
for  the  ground‐truth  situation.  These  on‐site  surveys  are  based  on  specially 
designed survey forms and were executed by experienced and skilled engineers 
on the field.  
 
The  objective  of  this  effort  is  to  ultimately  obtain  reliable  estimates  for  the 
number  of  trips  that  are  being  generated  from  second‐level  induced  traffic,  i.e. 
additional  trips  generated  by  extended  land  use  changes  due  to  improved 
accessibility.  In  this  case,  the  scope  of  the  study  is  primarily  commuter  traffic 
from  a  strip  of  land  around  a  major  road  infrastructure  project.  These  changes 
are  arguably  primarily  due  to  land  use  changes  and  subsequent 
socioeconomic  changes,  resulting  directly  from  the  infrastructure 
improvement. More buildings with more apartments result in more households 
that may make trips. Furthermore, changes in the cost of land might lead to the 
attraction  of  more  affluent  households  that  presumably  have  a  higher  car 
ownership  and  make  more  trips.  It  is  expected  that  –assuming  a  reasonable 
selection  of  the  strip  of  land  under  study‐  the  vast  majority  of  the  trips  will  be 
absorbed by the infrastructure project under study. 
 
The  main  steps  of  the  methodology  are  presented  next.  The  first  step  was  the 
selection  of  a  suitable  project  to  be  used  for  the  analysis.  The  criteria  for 
selection included: 
     • Time since the project was constructed (a more recent project would be 
          more advantageous, as the impact would be closer to the present time) 
     • Size of the project, ideally a large‐scale project. 
 
It quickly became apparent that the Attiki Odos motorway is an ideal candidate 
for this analysis, as it is a large‐scale project that was completed only a few years 
ago.  
 
Once the project has been identified, the next step is to define the analysis area. 
Considering the international literature and engineering judgment on this topic, 
a  strip  of land  extending  1.5km to  each of  the sides of the  project was  selected 
(i.e.  a  3km  wide  strip).  Clearly,  the  impact  of  such  a  project  in  shaping 
commuting behavior of neighboring areas extends well outside of this area, but 
this was selected as a conservative range.   
 
The  next  step  is  to  segment  the  study  area  into  analysis  zones  with  fairly 
uniform characteristics. The two main criteria for this segmentation are: 


                                                                                          page. 4
•   Building code regulations in the various municipalities. 
    •   Building  density  and  “saturation”,  i.e.  whether  the  area  has  reached  a 
        state  where  undeveloped  land  is  scarce  and  the  only  way  to  grow  is 
        vertically, or whether there is still room to grow horizontally. 
Based  on  the  intersection  of  the  above  two  classifications,  a  number  of  fairly 
homogeneous analysis zones is developed, for which the analysis will take place. 
 
The  last  requirement  for  the  performance  of  the  on‐site  surveys  is  the  design 
and validation of the forms. Suitable forms have been developed, based on the 
international literature and the experience of the project team. These forms were 
used by skilled and experienced engineers who recorded the required data in a 
series of field visits in the covered areas. The surveying engineers collected data 
such as the number of buildings per block, the number of floors per building and 
the number of apartments (and hence households) per floor. Prior to the actual 
on‐site  surveys,  a  round  of  pilot  evaluation  took  place,  where  the  forms  were 
used for surveying a couple areas. Based on the feedback, minor improvements 
were made to the forms, resulting to the final forms that were used for the on‐
site surveys. One such improvement was the addition of an area in the form for 
the inclusion of a digital photo of the surveyed area.  
 
Following  the  completion  of  the  on‐site  surveys,  the  data  were  analyzed, 
validated,  and  verified.  The  process  included  tabulation  of  the  data  in 
appropriately designed tables, and analysis using reality checks.  
 
The  next  step,  once  all  the  data  has  been  collected,  is  to  use  the  collected  data 
from  the  surveys  and  the  aerial  photographs  (e.g.  number  of  buildings  per 
analysis zone) to observe abrupt land‐use changes and estimate changes in the 
number of households.  
 
 
Clearly,  this  kind  of  work  involves  several  assumptions.  The  general  direction 
that was followed was towards making conservative assumptions that would 
lead  to  an  underestimation  of  the  impacts  of  the  new  infrastructure.  This 
would  add  an  extra  layer  of  confidence  in  the  findings,  as  the  result  of  the 
surveys  would  clearly  underestimate  the  impacts.  For  example,  in  the 
computation  of  the  change  in  the  number  of  households  around  Attiki  Odos 
between the years 2000 and 2008 (present), two assumptions (leading to clear 
underestimation) were made: 
    • For  a  large  part  of  the  influence  zone  (more  than  half),  in  which  the 
        changes were not dramatic, the number of households was held constant. 
        This  includes  both  well  built‐up  areas,  such  as  parts  of  Marousi,  Vrilisia, 
        and  Halandri,  and  less  developed  areas  (such  as  parts  of  Elefsina, 
        Aspropirgos and Spata). 
    • For the parts of the influence zone for which the change in the number of 
        buildings  between  2000  and  2008  was  computed,  the  number  of 
        households  per  building  was  assumed  to  be  constant  (for  the 
        computation of the change in the number of households).  
 



                                                                                        page. 5
3.2. Influence of Attiki Odos on residential development  
 
The survey focused only on a subset of the influence zone, for which the impact 
was  more  evident.  The  results  are  then  aggregated  with  the  counts  from  the 
remainder  of  the  influence  zone,  with  the  assumption  that  these  other  zones 
were  largely  saturated  and  the  increase  in  households  during  this  period  has 
been zero. Clearly, this is a very conservative approach.  
 
Figure  1  outlines  the  survey  results  for  the  surveyed  zones  around  the  Attiki 
Odos  motorway.  A  closer  examination  at  these  change  rates  reveals  (or  rather 
supports empirically) some interesting patterns. For example, areas that were 
already  well­built­up  prior  to  the  operation  of  the  Attiki  Odos  motorway, 
such as Marousi, Halandri and Agia Paraskevi, show more moderate growth rates 
(still around or even exceeding 20% annually for a period of 8 consecutive 
years),  while  areas  that  were  less  developed  and  had  more  room  for 
growth (e.g. Elefsina, Aspropirgos and Ano Liosia) show annual growth rates 
exceeding 50%.  
 
 




                                                                                                   
Figure  1.  Survey  results  for  zone  influenced  by  Attiki  Odos.  Number  of  households  per 
survey zone (top); annual change in household number per surveyed zone (bottom). 
 
 


                                                                                          page. 6
Using household data (showing the exact number of households and population 
per  building  block)  from  the  National  Statistical  Service  of  Greece  (ESYE)  for 
2000, the number of households in the influence zone in 2000 was 83.802, with 
30.222 of them in the areas that showed further growth and 53.850 in the areas 
that were excluded from the survey (and therefore conservatively assumed that 
the number of households remained constant). The number of households in the 
surveyed  zones,  as  computed  for  the  2008  situation  (using  the  number  of 
buildings from 2006), was found to be equal to 87.458, bringing the total number 
of  households  for the  entire influence zone (of  1.5km)  for  2008 (using data  for 
2006  for  the  areas  that  were  not  explicitly  surveyed3)  to  141.038  households. 
Therefore, a total increase of 68% in households was recorded over a period of 8 
years, which translates to an annual increase in households equal to 8.5% for 
the entire influence zone.  
 

4. Findings
 
In this paper, a synthesis on the literature on the irregularities in the output of 
transport  planning  models’  forecasts  for  capital  infrastructure  planning 
decisions  is  presented,  along  with  some  empirical  evidence  supporting  it  and 
shedding  some  light  into  it.  Several  directions  can  be  outlined  for  dealing  with 
these limitations, including: 
    • Activity  based  modeling:  which  can  be  used  to  improved  forecasting 
        models  incrementally  by  integrating  more  land  use  factors,  such  as  mix, 
        connectivity  and  design,  and  by  incorporating  feedback  loops  between 
        steps to recognize reciprocal impacts (Litman, 2005). 
    • Dealing  with  uncertainty:  several  researchers  (e.g.  Zhao  and  Kockelman, 
        2002, and Beser Hugosson, 2004, 2005) study the problem of how a given 
        transport model cannot only produce a central estimate of traffic volume 
        or revenues, but also uncertainty margins around these. 
    • Bridging  the  gap  between  state‐of‐the‐art  and  state‐of‐the‐practice: 
        Sammer (2006) identifies several reasons for this, including the demand 
        for  low‐cost  solutions,  increasingly  complex  (and  therefore  increasingly 
        obscure)  transport  modeling  software,  and  the  lack  of  available  quality 
        standards and procedures. 
 
 

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Beser  Hugosson,  M.:  Quantifying  uncertainties  in  the  SAMPERS  long  distance 
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Beser  Hugosson,  M.:  Quantifying  uncertainties  in  a  national  forecasting  model. 
Transportation Research A. 39A(6), 531–547 (2005)  
                                                        
3This leads to a conservative underestimation of the households for the present 

situation,  since  it  ignores  the  extra  development  that  took  place  in  the  last  few 
years (2006‐2008) in these areas. 


                                                                                      page. 7
 
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Zhao,  Y.,  Kockelman,  K.M.:  The  propagation  of  uncertainty  through  travel 
demand models: an exploratory analysis. Annals of Regional Science. 361, 145–
163 (2002)  
 




                                                                                    page. 8

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Irregularities in Traffic Forecasts

  • 1.   Paper submitted for the Proceedings of the  2nd International Symposium on Freeway and Tollway Operations  Honolulu, Hawaii – June 21‐24, 2009      Irregularities  in  the  output  of  transport  planning  models’  forecasts  for  capital infrastructure planning decisions    C. Antoniou1, B. Psarianos1, and W. Brilon2    Abstract    In  this  paper,  evidence  from  the  literature  on  the  inaccuracy  of  forecasts  from  transport planning models is presented and its impact on capital infrastructure  planning  decision‐making  is  demonstrated.  Empirical  evidence  suggests  that  forecasts  used  for  major  planning  decisions  internationally  have  been  found  to  be rather inaccurate (when comparing forecast flows with actually realized flows  after  time  passed).  Evidence  of  these  irregularities  in  the  case  of  a  major  expressway  infrastructure  project  in  Southern  Greece  is  presented,  providing  a  typical example of a country with an inadequate freeway network. Data from the  immediate  impact  zone  of  the  Attiki  Odos  tollway  in  the  metropolitan  area  of  Athens  are  used  to  demonstrate  that  the  project  resulted  in  a  considerable  change  in  the  land  use  patterns  and  density,  resulting  in  the  generation  of  additional traffic flows. Having demonstrated the need for re‐thinking how long‐ term  traffic  is  forecast,  suitable  recommendations  for  promising  directions  are  made. Dealing with uncertainty is one key aspect that can be easily incorporated  to existing forecasting tools. Furthermore, the need for more detailed and area‐ specific models, e.g. through the integration of activity‐based modeling, specific  mobility patterns and demands etc. are also outlined.    1. Introduction  Transportation planning and forecasting models are used as the basis for capital  infrastructure decisions. Quite often, however, the results of these models show  considerable  irregularities,  when  compared  with  the  actual  traffic  observed  when the forecast horizon has passed. This does not imply that the models or the  modelers  underperformed,  but  rather  that  there  are  some  inherent  difficulties  that  may  not  be  always  taken  into  account.  The  objective  of  this  paper  is  to  provide  some  insight  into  these  difficulties,  through  a  review  of  related  literature, and then attempt to quantify the impact of one such factor (the land‐ use – transport interaction) through an application in the Attiki Odos motorway  in the Athens, Greece, area.                                                           1  Laboratory  of  Transportation  Engineering,  National  Technical  University  of  Athens,  9  Heroon  Polytechniou, GR‐15780 Athens, Greece  Tel: +30 210 7722783, fax: +30 210 7722629, email: antoniou@central.ntua.gr (C. Antoniou)   Tel: +30 210 7722628, fax: +30 210 7722629, email: bpsarian@mail.ntua.gr (B. Psarianos)   2 Lehrstuhl für Verkehrswesen, Ruhr‐Universität Bochum, D ‐ 44780 Bochum, Germany  Tel. +49 (0)234 322 5936, Fax: + 49 (0)234 32 14 151, e­mail: verkehrswesen@rub.de  page. 1
  • 2.     According  to  Rodier  (2004),  it  is  widely  acknowledged  that  forecasts  produced  by  travel  and  emission  models  are  typically  inaccurate;  it  is  not  uncommon  to  find  large  differences  between  predicted  and  actual  outcomes.  Some  transportation  professionals  believe  that  current  state‐of‐the‐art  methods  can  forecast  emissions  with  an  accuracy  of  plus  or  minus  15  percent  to  30  percent  (Chatterjee  et  al,  1997).  Rodier  (2004)  also  concludes  that  recent  evidence  for  the induced travel hypothesis has increased concerns over the limited ability of  most  regional  travel  demand  models  to  represent  how  an  increase  in  roadway  supply reduces the time cost of travel and, to the extent that demand is elastic,  increases the quantity of travel demanded.     Parthasarathi and Levinson (2009) note that while research efforts have focused  on improving the technical aspects of a typical four‐step transportation planning  model, few studies have evaluated the model accuracy by comparing forecasts to  actual  traffic  counts.  The  analysis  indicated  that  traffic  forecasts  on  61.5%  of  the  links  were  underestimated  compared  to  the  actual  traffic  counts  and  the  forecasts  were  more  accurate  for  higher  volume  roadways.  Parthasarathi  and  Levinson (2009) also evaluate the accuracy of demand forecasts using a sample  of  recently  completed  projects  in  Minnesota  (with  a  horizon  forecast  year  of  2010 or earlier) and identify the factors influencing the inaccuracy in forecasts.  The analysis indicates a general trend of underestimation in roadway traffic  forecasts with factors such as highway type and functional classification playing  an  influencing  role.  Roadways  with  higher  volumes  and  higher  functional  classifications such as freeways are subject to more severe underestimation  compared to lower volume roadways/functional classifications.    An  explanation  for  the  underestimation  seen  in  forecasts,  specifically  road  forecasts,  can  be  attributed  to  the  non­incorporation  of  induced  traffic  into  the  model  forecasting  procedure  (Noland,  2001).  The  theory  of  induced  demand  states  that  increases  in  highway  capacity  induces  additional  growth  in  traffic  resulting  in  increased  levels  of  vehicle  traffic.  From  an  economic  perspective,  the  travel  demand  increases  as  the  cost  of  travel  decreases  due  to  capacity  improvements  resulting  in  an  elasticity  of  demand  associated  with  travel (Noland and Lem, 2000).     Flyvberg et al. (2006) present results from a large‐scale study of traffic forecasts  in transportation infrastructure projects, using a sample covering 210 projects in  14  nations  worth  US$58  billion.  The  study  shows  that  forecasters  generally  do  a  poor  job  of  estimating  the  demand  for  transportation  infrastructure  projects.  For  72%  of  rail  projects,  forecasts  are  overestimated  by  more  than  two‐thirds.  For  50%  of  road  projects,  the  difference  between  actual  and  forecasted  traffic  is  more  than  ±20%;  for  25%  of  road  projects,  the  difference is larger than ±40%.         page. 2
  • 3. 2. Factors affecting inaccuracy of transportation forecasting    Sammer  (2006)  observes  that  while  the  currently  available  modelling  approaches are considerably more flexible and powerful than those of the 1990s,  there  is  considerable  evidence  that  the  gap  between  state­of­the­art  theory  and  practice,  i.e.  the  actual  modelling  of  transport,  is  widening.  One  of  the  implications of this observation is that trust in the validity of modelling results is  decreasing  significantly.  Concluding,  Sammer  (2006)  summarizes  the  problems  in  transportation  forecasting  as:  (i)  the  models,  and  especially  the  produced  forecasts,  suffer  from  the  “black­box  effect”,  as  they  cannot  be  followed  through and understood, (ii) many of the models are no longer state‐of‐the‐art,  (iii)  there  is  little  or  no  evidence  for  the  validity  of  the  input  data  used  or  how  the  model  was  calibrated,  and  (iv)  the  results  are  presented  as  point  estimates,  rather  than  interval  estimates  based  on  a  probability  function,  with  confidence limits specified.      Transport models are (often complex) approximations of very complex systems.  Therefore,  a  number  of  errors  can  occur  which  may  have  an  impact  on  the  accuracy of the forecast results (Sammer, 2006):  • Measurement errors;  • Random errors;  • Forecast errors due to the input data used;  • Computational and application errors;  • Model specification errors;  • Transferability  errors  (when  attempting  to  apply  a  model  calibrated  in  one  region to another)  • Aggregation and disaggregation errors.  These  errors  may  either  result  in  additive  (or  even  multiplicative)  effects,  or  cancel out (thus hiding potentially important model shortcomings).       Litman (2005) examines how various land use factors such as density, regional  accessibility, mix and roadway connectivity affect travel behaviour, including per  capita  vehicle  travel,  mode  split  and  non‐motorized  travel.  Litman  concludes  that  land  use  factors  can  have  significant  impacts  on  travel  patterns,  but  that  current  transportation  models  are  not  accurate  at  predicting  their  effects.     Wegener  and  Fuerst  (1999)  indicate  that  the  impacts  of  transport  policies  on  transport  patterns  are  clearer  and  stronger  compared  to  the  interplay  of  land  use  and  transport.  While  travel  cost  and  travel  time  have  a  negative  impact  on  both trip length and trip frequency, accessibility has a positive impact on trip  length  and  frequency.  Mode  choice  is  dependent  upon  the  relative  attractiveness of a mode compared to all other modes. The fastest and cheapest  mode  is  likely  to  have  the  highest  modal  share.  In  general,  the  theoretical  considerations support the conclusion that the impact of 'pull' measures, i.e. land  use measures, is much weaker than the impact of 'push' measures, i.e. increases  in travel time, travel cost etc.     page. 3
  • 4. 3. An empirical analysis of the changes in land-use and traffic patterns due to the Attiki Odos Motorway In  this  section,  an  empirical  analysis  of  the  impact  of  land‐use  into  traffic  patterns due to the Attiki Odos motorway in the Athens area is presented.   3.1. Methodology for on‐site surveys for data‐collection  One of the big challenges associated with modeling and other estimation efforts  lies  in  the  original  data  input.  In  this  case,  we  have  relied  in  a  wide  variety  of  sources  for  data  collection.  In  the  core  of  this  effort,  however,  is  a  set  of  coordinated  on­site  surveys,  aimed  at  providing  first‐hand,  reliable  evidence  for  the  ground‐truth  situation.  These  on‐site  surveys  are  based  on  specially  designed survey forms and were executed by experienced and skilled engineers  on the field.     The  objective  of  this  effort  is  to  ultimately  obtain  reliable  estimates  for  the  number  of  trips  that  are  being  generated  from  second‐level  induced  traffic,  i.e.  additional  trips  generated  by  extended  land  use  changes  due  to  improved  accessibility.  In  this  case,  the  scope  of  the  study  is  primarily  commuter  traffic  from  a  strip  of  land  around  a  major  road  infrastructure  project.  These  changes  are  arguably  primarily  due  to  land  use  changes  and  subsequent  socioeconomic  changes,  resulting  directly  from  the  infrastructure  improvement. More buildings with more apartments result in more households  that may make trips. Furthermore, changes in the cost of land might lead to the  attraction  of  more  affluent  households  that  presumably  have  a  higher  car  ownership  and  make  more  trips.  It  is  expected  that  –assuming  a  reasonable  selection  of  the  strip  of  land  under  study‐  the  vast  majority  of  the  trips  will  be  absorbed by the infrastructure project under study.    The  main  steps  of  the  methodology  are  presented  next.  The  first  step  was  the  selection  of  a  suitable  project  to  be  used  for  the  analysis.  The  criteria  for  selection included:  • Time since the project was constructed (a more recent project would be  more advantageous, as the impact would be closer to the present time)  • Size of the project, ideally a large‐scale project.    It quickly became apparent that the Attiki Odos motorway is an ideal candidate  for this analysis, as it is a large‐scale project that was completed only a few years  ago.     Once the project has been identified, the next step is to define the analysis area.  Considering the international literature and engineering judgment on this topic,  a  strip  of land  extending  1.5km to  each of  the sides of the  project was  selected  (i.e.  a  3km  wide  strip).  Clearly,  the  impact  of  such  a  project  in  shaping  commuting behavior of neighboring areas extends well outside of this area, but  this was selected as a conservative range.      The  next  step  is  to  segment  the  study  area  into  analysis  zones  with  fairly  uniform characteristics. The two main criteria for this segmentation are:  page. 4
  • 5. Building code regulations in the various municipalities.  • Building  density  and  “saturation”,  i.e.  whether  the  area  has  reached  a  state  where  undeveloped  land  is  scarce  and  the  only  way  to  grow  is  vertically, or whether there is still room to grow horizontally.  Based  on  the  intersection  of  the  above  two  classifications,  a  number  of  fairly  homogeneous analysis zones is developed, for which the analysis will take place.    The  last  requirement  for  the  performance  of  the  on‐site  surveys  is  the  design  and validation of the forms. Suitable forms have been developed, based on the  international literature and the experience of the project team. These forms were  used by skilled and experienced engineers who recorded the required data in a  series of field visits in the covered areas. The surveying engineers collected data  such as the number of buildings per block, the number of floors per building and  the number of apartments (and hence households) per floor. Prior to the actual  on‐site  surveys,  a  round  of  pilot  evaluation  took  place,  where  the  forms  were  used for surveying a couple areas. Based on the feedback, minor improvements  were made to the forms, resulting to the final forms that were used for the on‐ site surveys. One such improvement was the addition of an area in the form for  the inclusion of a digital photo of the surveyed area.     Following  the  completion  of  the  on‐site  surveys,  the  data  were  analyzed,  validated,  and  verified.  The  process  included  tabulation  of  the  data  in  appropriately designed tables, and analysis using reality checks.     The  next  step,  once  all  the  data  has  been  collected,  is  to  use  the  collected  data  from  the  surveys  and  the  aerial  photographs  (e.g.  number  of  buildings  per  analysis zone) to observe abrupt land‐use changes and estimate changes in the  number of households.       Clearly,  this  kind  of  work  involves  several  assumptions.  The  general  direction  that was followed was towards making conservative assumptions that would  lead  to  an  underestimation  of  the  impacts  of  the  new  infrastructure.  This  would  add  an  extra  layer  of  confidence  in  the  findings,  as  the  result  of  the  surveys  would  clearly  underestimate  the  impacts.  For  example,  in  the  computation  of  the  change  in  the  number  of  households  around  Attiki  Odos  between the years 2000 and 2008 (present), two assumptions (leading to clear  underestimation) were made:  • For  a  large  part  of  the  influence  zone  (more  than  half),  in  which  the  changes were not dramatic, the number of households was held constant.  This  includes  both  well  built‐up  areas,  such  as  parts  of  Marousi,  Vrilisia,  and  Halandri,  and  less  developed  areas  (such  as  parts  of  Elefsina,  Aspropirgos and Spata).  • For the parts of the influence zone for which the change in the number of  buildings  between  2000  and  2008  was  computed,  the  number  of  households  per  building  was  assumed  to  be  constant  (for  the  computation of the change in the number of households).     page. 5
  • 6. 3.2. Influence of Attiki Odos on residential development     The survey focused only on a subset of the influence zone, for which the impact  was  more  evident.  The  results  are  then  aggregated  with  the  counts  from  the  remainder  of  the  influence  zone,  with  the  assumption  that  these  other  zones  were  largely  saturated  and  the  increase  in  households  during  this  period  has  been zero. Clearly, this is a very conservative approach.     Figure  1  outlines  the  survey  results  for  the  surveyed  zones  around  the  Attiki  Odos  motorway.  A  closer  examination  at  these  change  rates  reveals  (or  rather  supports empirically) some interesting patterns. For example, areas that were  already  well­built­up  prior  to  the  operation  of  the  Attiki  Odos  motorway,  such as Marousi, Halandri and Agia Paraskevi, show more moderate growth rates  (still around or even exceeding 20% annually for a period of 8 consecutive  years),  while  areas  that  were  less  developed  and  had  more  room  for  growth (e.g. Elefsina, Aspropirgos and Ano Liosia) show annual growth rates  exceeding 50%.         Figure  1.  Survey  results  for  zone  influenced  by  Attiki  Odos.  Number  of  households  per  survey zone (top); annual change in household number per surveyed zone (bottom).      page. 6
  • 7. Using household data (showing the exact number of households and population  per  building  block)  from  the  National  Statistical  Service  of  Greece  (ESYE)  for  2000, the number of households in the influence zone in 2000 was 83.802, with  30.222 of them in the areas that showed further growth and 53.850 in the areas  that were excluded from the survey (and therefore conservatively assumed that  the number of households remained constant). The number of households in the  surveyed  zones,  as  computed  for  the  2008  situation  (using  the  number  of  buildings from 2006), was found to be equal to 87.458, bringing the total number  of  households  for the  entire influence zone (of  1.5km)  for  2008 (using data  for  2006  for  the  areas  that  were  not  explicitly  surveyed3)  to  141.038  households.  Therefore, a total increase of 68% in households was recorded over a period of 8  years, which translates to an annual increase in households equal to 8.5% for  the entire influence zone.     4. Findings   In this paper, a synthesis on the literature on the irregularities in the output of  transport  planning  models’  forecasts  for  capital  infrastructure  planning  decisions  is  presented,  along  with  some  empirical  evidence  supporting  it  and  shedding  some  light  into  it.  Several  directions  can  be  outlined  for  dealing  with  these limitations, including:  • Activity  based  modeling:  which  can  be  used  to  improved  forecasting  models  incrementally  by  integrating  more  land  use  factors,  such  as  mix,  connectivity  and  design,  and  by  incorporating  feedback  loops  between  steps to recognize reciprocal impacts (Litman, 2005).  • Dealing  with  uncertainty:  several  researchers  (e.g.  Zhao  and  Kockelman,  2002, and Beser Hugosson, 2004, 2005) study the problem of how a given  transport model cannot only produce a central estimate of traffic volume  or revenues, but also uncertainty margins around these.  • Bridging  the  gap  between  state‐of‐the‐art  and  state‐of‐the‐practice:  Sammer (2006) identifies several reasons for this, including the demand  for  low‐cost  solutions,  increasingly  complex  (and  therefore  increasingly  obscure)  transport  modeling  software,  and  the  lack  of  available  quality  standards and procedures.      References   Beser  Hugosson,  M.:  Quantifying  uncertainties  in  the  SAMPERS  long  distance  forecasting system. Paper presented at the WCTR 2004, Istanbul (2004)     Beser  Hugosson,  M.:  Quantifying  uncertainties  in  a  national  forecasting  model.  Transportation Research A. 39A(6), 531–547 (2005)                                                            3This leads to a conservative underestimation of the households for the present  situation,  since  it  ignores  the  extra  development  that  took  place  in  the  last  few  years (2006‐2008) in these areas.  page. 7
  • 8.   Chatterjee, A., Miller, T. L., Philpot, J. W., Wholley, T. F., Guensler, R., Hartgen, D.,  Margiotta,  R.  A.,  and  Stopher,  P.  R.,  Improving  Transportation  Data  for  Mobile  Source  Emission  Estimates,  Transportation  Research  Board,  National  Research  Council, National Cooperative Highway Research Program Report 394, National  Academy Press, 1997.     Flyvbjerg,  B.,  M.  K.  Skamris  Holm,  and  S.  L.  Buhl  (2006).  Inaccuracy  in  traffic  forecasts. Transport Reviews, Vol. 26, No. 1, 1‐24, January 2006.    Litman, T.A. Land Use Impacts on Transport. How Land Use Factors Affect Travel  Behavior.  Victoria  Transport  Policy  Institute,  November  16,  2005.  (available  online: http://www.dot.wisconsin.gov/localgov/docs/victoria‐transport.pdf)     Noland, R. (2001), “Relationships between highway capacity and induced vehicle  travel”, Transportation Research Part A , Vol. 35, Elsevier, pp. 47–72.     Noland, R. and Lem, L. (2000), “Induced travel: A review of recent literature and  the implications for transportation and environmental policy”, Appraisal of Road  Transport Initiatives: Proceedings of Seminar D Held at the European Transport  Conference. (www.cts.cv.ic.ac.uk/staff/wp2‐noland.pdf).    Parthasarathi,  P.,  and  D.  Levinson.  (2009).  Post‐Construction  Evaluation  of  Forecast  Accuracy.  Final  Report  Mn_DOT2009‐11,  Minnesota  Department  of  Transportation, February 2009 .    Rodier,  C.  J.  (2004).  Verifying  the  accuracy  of  regional  models  used  in  transportation  and  air  quality  planning:  A  case  study  in  the  Sacramento,  California, Region. Proceedings of the 83rd Annual Meeting of the Transportation  Research Board, Washington, D.C., January.    Sammer,  G.  (2006).  The  gap  between  theory  and  application  when  modelling  transport  –  The  necessity  of  quality  standards.  Proceedings  of  the  11th  International Conference on Travel Behaviour Research, Kyoto, 16‐20 August.    Wegener, M. and F. Fuerst (1999). Land‐Use Transport Interaction: State of the  Art.  Deliverable  2a  of  the  project  TRANSLAND  (Integration  of  Transport  and  Land  Use  Planning)  of  the  4th  RTD  Framework  Programme  of  the  European  Commission. Institute fuer Raumplanung, Universitaet Dortmund.    Zhao,  Y.,  Kockelman,  K.M.:  The  propagation  of  uncertainty  through  travel  demand models: an exploratory analysis. Annals of Regional Science. 361, 145– 163 (2002)     page. 8