United States
                    Environmental Protection
                    Agency
Atmospheric Sciences
Research Laboratory
Research Triangle Park NC 27711
                    Research and Development
EPA/600/S8-87/058  Mar. 1988
vxEPA         Project  Summary
                    User's  Guide to  the  Complex
                    Terrain  Dispersion  Model
                    Robert J. Paine, David G. Strimaitis, Michael G. Dennis,
                    Robert J. Yamartino, Michael T. Mills, and Elizabeth M. Insley
                      The Complex Terrain Dispersion
                    Model (CTDM) is a refined  air quality
                    model for use in stable and neutral
                    conditions in complex terrain  applica-
                    tions. Its use of meteorological  input
                    data and terrain information is different
                    than current EPA models; considerable
                    detail for both types of input data are
                    required and are supplied by preproces-
                    sors specifically designed for CTDM.
                    CTDM requires the parameterization of
                    individual hill shapes using the terrain
                    preprocessor and the  association of
                    each model receptor with a particular
                    hill (except for receptors in flat terrain,
                    which CTDM can also handle).
                      A central feature of CTDM is its use
                    of a critical dividing-streamline height
                    (Hc) to separate the flow in the vicinity
                    of a hill into two separate layers. Flow
                    in the upper layer has sufficient kinetic
                    energy to pass over the top of the hill
                    while streamlines in the lower layer are
                    constrained to flow in a  horizontal
                    plane  around  the hill. Two separate
                    components  of CTDM  compute
                    ground-level concentrations resulting
                    from plume material in each of these
                    flows: LIFT handles the flow above Hc,
                    and WRAP handles the flow below Hc.
                      Hourly profiles of wind and temper-
                    ature measurements are used by CTDM
                    to compute plume rise, the value of Hc,
                    and the Froude number above Hc. The
                    profiles of turbulence data (ffeor crv and
                    <7W values) are used to compute plume
                    ay and crz values at plume height.
                      The model will calculate on an hourly
                    basis how the plume  trajectory and
                    shape are deformed by each hill. The
computed concentration at each recep-
tor is then derived from the receptor
position on the hill and the resultant
plume position and shape.
  The CTDM user guide is divided into
two volumes: Volume 1 describes the
model and how to use it, while Volume
2 contains code listings. Two auxiliary
user manuals describe the CTDM
terrain   and  meteorological  pre-
processors.

  This Project Summary  was devel-
oped by EPA's Air and Energy Engi-
neering Research Laboratory. Research
Triangle  Park, NC. to announce key
findings of the research project that is
fully documented in two separate
volumes of the same title (see Project
Report ordering information at back).

Introduction
  The Complex Terrain Model Develop-
ment (CTDM) project was initiated by the
U.S. Environmental Protection Agency
(EPA) to develop a practical refined plume
model for elevated point sources near
complex terrain. The result of this effort
is the CTDM, which this user manual
describes.
  Complex terrain models presently
recommended for regulatory use by EPA
have been designated as  screening
models, as they tend  to  overpredict
ambient concentrations and can there-
fore screen out situations which may not
require further detailed analyses. These
screening models (VALLEY, COMPLEX I,
SHORTZ,  and RTDM are deficient  in
several areas:

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• Deflection and diffusion of plumes in
   the  vertical  is  crudely treated  by
   means of a plume height factor.
• Only the third-level screening model,
   RTDM, incorporates the concept of a
   dividing-streamline height.        x

• The screening models can accept only
   one  level of input meteorology. Wind
   speed profiles are parameterized as a
   function of  stability class.  Wind
   direction is not allowed to vary with
   height.
• Explicit calculations of cry and az from
   turbulence intensities are not done in
   the screening models.
• Plumes cannot be deflected  horizon-
   tally around obstacles; a straight-line
   trajectory is assumed in the screening
   models.
• Screening models for complex terrain
   applications generally employ sector
   averaging in  the horizontal  for con-
   centration calculations because of the
   inability  of the model to depict the
   actual plume  trajectory.
• Plumes embedded  in a stable  layer
   above  a shallow  unstable  surface
   layer are ignored.

• The  screening models make limited
   use of knowledge of the terrain shape.

CTDM addresses these deficiencies:

• The  structure of the two-layer flow
   (above/below the dividing-streamline
   height) is explicit in the formulation,
   and plume material that straddles the
   interface remains  in  the  respective
   layers (the plume is not treated as if
   it were all in one layer or the other).
• Above HCl the material is deflected and
   distored, and  the rate of dispersion is
   altered.  Below  Hc, the stagnation
   streamline divides the flow, and only
   material  that diffuses onto the  stag-
   nation streamline is able to reach the
   surface of the hill. The stagnation
   streamline and the  concentration
   pattern wraps around the  terrain.
   Plumes that  lie to one side  of  stag-
   nation streamline  pass around the
   terrain.
• The rate of plume growth depends on
   the turbulence and, in the case of az,
   it also  depends  on the degree  of
   stratification. Sector averaging in the
   lateral direction is not used.
  The focus of the model development
effort to date  has been  on the  stable
plume impingement problem. As a result,
CTDM  contains  algorithms that are
suitable for neutral and stably-stratified
flows (i.e.,  Pasquill-Gifford stability
classes,  D,  E, and  F).   However, the
sequential hourly datasets  required for
regulatory applications  contain  hours
characterized by  classes A, B, and C as
well. Rather than include an untested
algorithm for these classes, or explicity
include  an  algorithm  from an existing
screening model, CTDM writes out "null"
concentrations (-999) for these hours.

Model Applicability and
Technical  Limitations
  The CTDM is a point-source Gaussian
plume  dispersion model designed to
estimate hourly-averaged concentra-
tions of plume  material at receptors near
an isolated hill or near  a well-defined
segment of  an array of  hills. Primary
emphasis is given to  simulating situa-
tions in which the flow toward the hill
is stably stratified, and  in which the
plume has  not encountered significant
terrain  upwind.  Receptors on  terrain
downwind of a  point source will generally
be associated with the greatest esti mates
of ground-level concentrations in stable
conditions.
  The following restrictions and assump-
tions about CTDM should be understood:

• CTDM contains no wake algorithms
   for simulating  the  mixing and  recir-
   culation found in cavity zones in the
   lee of a hill.
• CTDM contains no global flow calcu-
   lation that accounts for the presence
   of many hills. The path taken by a
   plume through an array of hills cannot
   be simulated  by the model. It  relies
   on measurements of the flow obtained
   in the neighborhood of the source to
   define the incident flow field for each
   of  the  terrain  segments   inde-
   pendently.
• All hills that are explicitly modeled are
   done so  in  isolation; any changes to
   the plume size caused by one hill are
   not  carried forward  to  subsequent
   simulations downwind.
• For situations when an individual hill
   is difficult to isolate from a complex
   terrain structure,   caution must be
   used in interpreting the CTDM results.
• Real terrain  features are  approxil
   mated by ideal shapes. CTDM consid-
   ers Gaussian shaped hills.
• CTDM does not simulate calm mete-
   orological periods.
• CTDM assumes that the meteorolog-
   ical  data are representative of the
   entire averaging period, and apply to
   the  entire  spatial domain.  Spatial
   variability  resolved  by an  array of
   meteorological towers cannot be used
   directly in the model.
• CTDM is designed for neutral to stable
   flow conditions; therefore the model
   does not predict concentrations  dur-
   ing  unstable hours when  any plume
   is within the convective mixed layer.
• Hill slopes are assumed not to exceed
   15°, so that the linearized equations
   of motion for Boussinesq flow are
   applicable.

These restrictions are consistent with the
primary purpose of  the model, namely,
that  of estimating pollutant  concentra-
tions on nearby  terrain  during stable
(generally  nighttime)  atmospheric
conditions.

Overview of CTDM
Components
  The CTDM package consists of:

• the Complex Terrain Dispersion Mode
• a  terrain preprocessor (Mills et al.
   1987)
• a meteorological preprocessor (Paine
   1987)
• a receptor coordinate generator
• a  graphical concentration  displa
   program
• an interactive program which allow
   the user to modify model inputs easil
   and  run CTDM in a case-study mode

  All the programs, except the thre
graphics programs, PLOTCON,  RECGEI
and CHIDIS, are written in FORTRAN 11
The  graphics  programs are  written i
BASIC.

  The  CTDM  terrain preprocessor  i
made up of 3 programs which  proces
digitized contour data to provide  hi
shape  parameters in a format suitabl
for direct  input to CTDM.  The  fin
program, FITCON, asks the user to defir
a hill in terms of its  maximum elevatic
and the (x,y) coordinates of the hill inpi

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 from a master file. After evaluation and
 editing, each contour is  processed by
 numerical  integration to determine the
 following  parameters for  an equivalent
 ellipse: semi-major and semi-minor axis
 lengths;  contour centroid coordinates;
 and the orientation  of the ellipse.  The
 parameters  are  input  to the second
 terrain  preprocessor program,  HCRIT,
 which determines, for the portion of the
 hill above several given elevations, the
 best-fit inverse  polynominal  profiles
 along the  hill  major and minor axes.
 CTDM uses the contour representations
 to provide  hill shape information  above
 the critical dividing streamline height for
 each hour and each hill using interpo-
 lation between two look-up table values.
 The third program, PLOTCON, generates
 screen displays to aid in the evaluation
 of the hill fitting process.
  The CTDM meteorological preproces-
 sor,  METPRO,  uses routine  measure-
 ments to estimate the vertical  structure
 of wind, temperature and turbulence in
 the  lower atmosphere using  surface
 layer similarity theory. Estimates  of the
 friction velocity, uğ, the Monin-Obukhov
 length, L, and the mixed layer height, h,
 are provided by METPRO to CTDM. In the
 absence of measurements of profiles of
 wind, temperature,  and  turbulence,
 these variables are  used by CTDM to
 compute values of wind,  temperature
 and turbulence at any height within the
 nocturnal surface layer.
  The receptor generator program, REC-
 GEN, in an interactive program written
 in BASIC which will compute receptor
 coordinate information  for  receptors
 along user selected  hill contours.  The
 program will  create a file containing the
 receptor  information which  can be
 directly input  to CTDM. RECGEN will also
 display the contour  lines  and receptor
 locations on  the  terminal  screen.  The
 user can easily add receptors in addition
 to those produced by RECGEN  using a
 text editor.
  The main CTDM program performs the
 plume transport and  dispersion calcula-
 tions for the entire period of simulation.
 It takes the files prepared by the  mete-
 orological  and terrain preprocessors
 together with the source  and receptor
 files, and executes under the control of
 the options specified in an input  file.
 Modeled concentrations can be stored in
 a binary or an ASCII output file, if desired.
 The  model lists all of the  control data
 describing the simulation,  and pertinent
 source, receptor, and terrain data  to the
output list file. In  case-study  mode.
extensive tables of selected variables are
also listed for computations performed
for each source, hill, and receptor.
  The concentration display postproces-
sor consists of two separate programs.
Both programs are interactive and will
ask the user for the necessary file names
and  input  data.  These programs will
display  on the  screen the  predicted
concentrations from CTDM on a map of
unedited hill contours.  Concentrations
for  a series of hours can be displayed
sequentially, but each hill must be done
individually.

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    Robert J. Paine, Michael G. Dennis, and Michael T. Mills are with ERT, Inc.,
      Concord MA 01742; David G. Strimaitis, Robert J. Yamartino, and Elizabeth
      M. Insley are with Sigma Research Corp., Lexington, MA 02173.
    Peter L. Finkelstein is the EPA Project Officer (see below).
    The complete report  consists of two volumes, entitled "User's Guide to the
      Complex Terrain Dispersion Model:"
      "Volume  1. Model Description and User Instructions," (Order No. PB 88-
      162 128/AS; Cost:  $19.95)
      "Volume  2. Model Code Listings," (Order No. PB 88-162 136/AS; Cost:
      $25.95)
    The above reports will be available only from: (cost subject to change)
            National Technical Information Service
            5285 Port Royal Road
            Springfield, VA 22161
            Telephone: 703-487-4650
    The EPA Project Officer can be contacted at:
            Atmospheric  Sciences Research Laboratory
            U.S. Environmental Protection Agency
            Research Triangle Park, NC 27711
United States
Environmental Protection
Agency
Center for Environmental Research
Information
Cincinnati OH 45268
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