Table of Contents - The Atmospheric Studies Group at TRC

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Section 10: POSTPROCESSORS Table 10-11 (Continued) Sample POSTUTIL Control File (POSTUTIL.INP) Input Group 1 -------------------------------------------------------------------------------- INPUT GROUP: 1 -- General run control parameters -------------- Starting date: Year (ISYR) -- No default ! ISYR = 1990 ! Month (ISMO) -- No default ! ISMO = 1 ! Day (ISDY) -- No default ! ISDY = 9 ! Hour (ISHR) -- No default ! ISHR = 5 ! Number of periods to process (NPER) -- No default ! NPER = 4 ! Number of species to process from CALPUFF runs (NSPECINP) -- No default ! NSPECINP = 7 ! Number of species to write to output file (NSPECOUT) -- No default ! NSPECOUT = 3 ! Number of species to compute from those modeled (must be no greater than NSPECOUT) (NSPECCMP) -- No default ! NSPECCMP = 2 ! When multiple files are used, a species name may appear in more than one file. Data for this species will be summed (appropriate if the CALPUFF runs use different source groups). If this summing is not appropriate, remove duplicate species from the file(s). Stop run if duplicate species names are found (MDUPLCT) Default: 0 ! MDUPLCT = 0 ! 0 = no (i.e., duplicate species are summed) 1 = yes (i.e., run is halted) Data for each species in a CALPUFF data file may also be scaled as they are read. This can be done to alter the emission rate of all sources that were modeled in a particular CALPUFF application. The scaling factor for each species is entered in Subgroup (2d), for each file for which scaling is requested. Number of CALPUFF data files that will be scaled (must be no greater than NFILES) (NSCALED) Default: 0 ! NSCALED = 0 ! 10-27
Section 10: POSTPROCESSORS Table 10-11 (Continued) Sample POSTUTIL Control File (POSTUTIL.INP) Input Group 1 Ammonia-Limiting Method Option to recompute the HNO3/NO3 concentration partition prior to performing other actions is controlled by MNITRATE. This option will NOT alter any deposition fluxes contained in the CALPUFF file(s). Three partition selections are provided. The first two are typically used in sequence (POSTUTIL is run more than once). The first selection (MNITRATE=1) computes the partition for the TOTAL (all sources) concentration fields (SO4, NO3, HNO3; NH3), and the second (MNITRATE=2) uses this partition (from the previous application of POSTUTIL) to compute the partition for individual source groups. The third selection (MNITRATE=3) can be used instead in a single POSTUTIL application if a file of background concentrations is provided (BCKGALM in Input Group 0). Required information for MNITRATE=1 includes: species NO3, HNO3, and SO4 NH3 concentration(s) met. data file for RH and T Required information for MNITRATE=2 includes: species NO3 and HNO3 for a source group species NO3ALL and HNO3ALL for all source groups, properly partitioned Required information for MNITRATE=3 includes: species NO3, HNO3, and SO4 for a source group species NO3, HNO3, SO4 and TNH3 from the background BCKGALM file If TNH3 is not in the background BCKGALM file, monthly TNH3 concentrations are used (BCKTNH3) Recompute the HNO3/NO3 partition for concentrations (MNITRATE) Default: 0 ! MNITRATE = 0 ! 0 = no 1 = yes, for all sources combined 2 = yes, for a source group 3 = yes, ALM application in one step SOURCE OF AMMONIA: Ammonia may be available as a modeled species in the CALPUFF files, and it may or may not be appropriate to use it for repartitioning NO3/HNO3 (in option MNITRATE=1 or MNITRATE=3). Its use is contolled by NH3TYP. When NH3 is listed as a processed species in Subgroup (2a), as one of the NSPECINP ASPECI entries, and the right option is chosen for NH3TYP, the NH3 modeled values from the CALPUFF concentration files will be used in the chemical equilibrium calculation. 10-28
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CALPUFF Modeling System Version 6 U
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Section 1: Introduction 7.5 CALWRF
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Section 1: Introduction List of Fig
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Section 1: Introduction Table 3-1:
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Section 1: Introduction introductio
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Section 1: Introduction CALMET Upd
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Section 1: Introduction To enhance
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Section 1: Introduction Meteorologi
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Section 1: Introduction OPTHILL uti
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Section 1: Introduction From CALPUF
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Section 1: Introduction Observation
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Section 1: Introduction Slope Flows
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Section 1: Introduction 1.5 Summary
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Section 1: Introduction technical o
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Section 8: CALMET Model Files (e.g.
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Section 8: CALMET Model Files Table
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Section 8: CALMET Model Files descr
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Section 8: CALMET Model Files range
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Section 8: CALMET Model Files recor
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Section 8: CALMET Model Files 8.10
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Section 8: CALMET Model Files 4 NUS
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Section 8: CALMET Model Files CALME
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Section 8: CALMET Model Files 8.1.1
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Section 8: CALMET Model Files ┌
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Section 8: CALMET Model Files 8.2 P
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Section 8: CALMET Model Files -----
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Section 8: CALMET Model Files 6 0 0
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Section 8: CALMET Model Files 3 1 1
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Section 8: CALMET Model Files IBHR
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Section 8: CALMET Model Files Multi
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Section 9: CALPUFF 9. CALPUFF The C
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Section 9: CALPUFF The control file
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Section 9: CALPUFF Table 9-1: Input
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Section 9: CALPUFF 17a,b Non-gridde
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Section 9: CALPUFF MASSBAL.DAT outp
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Section 9: CALPUFF d The filenames
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Section 9: CALPUFF >0 = File update
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Section 9: CALPUFF 0 = chemical tra
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Section 9: CALPUFF [DIAGNOSTIC FEAT
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Section 9: CALPUFF ! CSPEC = SO2 !
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Section 9: CALPUFF WGS-84 NAS-C NAR
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Section 9: CALPUFF for selected spe
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Section 9: CALPUFF ---------------
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Section 9: CALPUFF --------- ------
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Section 9: CALPUFF Input Group 11 O
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Section 9: CALPUFF (XLAIIN) Default
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Section 9: CALPUFF Minimum mixing h
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Section 9: CALPUFF Near-Surface dep
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Section 9: CALPUFF Sample CALPUFF C
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Section 9: CALPUFF -------- a Data
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Section 9: CALPUFF Number of buoyan
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Section 9: CALPUFF -------- a Data
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Section 9: CALPUFF Number of non-gr
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Section 9: CALPUFF 9-47
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Section 9: CALPUFF Table 9-3 (Conti
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Section 9: CALPUFF IOUTU IOVERS int
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Section 9: CALPUFF MSHEAR integer V
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Section 9: CALPUFF MDISP integer Me
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Section 9: CALPUFF MPDF integer Pro
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Section 9: CALPUFF IMFLX integer Co
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Section 9: CALPUFF BCKNH3(12) real
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Section 9: CALPUFF CDIV(2) real Div
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Section 9: CALPUFF *MDEPBC integer
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Section 9: CALPUFF BDOWN real Build
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Section 9: CALPUFF source is treate
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Section 9: CALPUFF (i.e., !END!). I
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Section 9: CALPUFF (i.e., !END!). I
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Section 9: CALPUFF terminator (i.e.
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Section 9: CALPUFF Table 9-3 (Concl
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Section 9: CALPUFF 9.2 Meteorologic
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Section 9: CALPUFF if(nssta.ge.1)th
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Section 9: CALPUFF Table 9-4: CALME
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Section 9: CALPUFF Table 9-4 (Concl
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Section 9: CALPUFF 4 b 6 ZTEMP real
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Section 9: CALPUFF 9 6 WSTAR real a
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Section 9: CALPUFF 14 6 IRH integer
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Section 9: CALPUFF variable dispers
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Section 9: CALPUFF Table 9-6: Sampl
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Section 9: CALPUFF NCOMM+6 * intege
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Section 9: CALPUFF Table 9-8 (conti
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Section 9: CALPUFF table. A descrip
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Section 9: CALPUFF Table 9-10: PLMM
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Section 9: CALPUFF 9.2.4 SURFACE.DA
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Section 9: CALPUFF Table 9-12: Samp
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Section 9: CALPUFF Table 9-13 (cont
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Section 9: CALPUFF Table 9-14: SURF
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Section 9: CALPUFF Table 9-14 (conc
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Section 9: CALPUFF Table 9-15 (cont
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Section 9: CALPUFF 9.3 Point Source
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Section 9: CALPUFF Table 9-17: PTEM
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Section 9: CALPUFF Table 9-17 (Cont
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Section 9: CALPUFF 9.4 Buoyant Area
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Section 9: CALPUFF Table 9-21: BAEM
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Section 9: CALPUFF . . . . . . . .
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Section 9: CALPUFF Table 9-23 (Conc
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Section 9: CALPUFF NCOMM+8 or 9 IEJ
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Section 9: CALPUFF Table 9-26: LNEM
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Section 9: CALPUFF * "NSE" elements
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Section 9: CALPUFF 9.7 Boundary Con
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Section 9: CALPUFF The model checks
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Section 9: CALPUFF 9.11 Site-Specif
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Section 9: CALPUFF Table 9-43: HILL
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Section 9: CALPUFF where the follow
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Section 9: CALPUFF 9.14 Mass Flux B
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Section 9: CALPUFF Table 9-49: FLUX
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Section 9: CALPUFF 9.15 CALPUFF Out
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Section 9: CALPUFF IF(NVL1.GT.0) RE
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Section 9: CALPUFF CONC.DAT File -
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Section 9: CALPUFF 9.15.4 Dry Flux
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Section 9: CALPUFF nxg = IESAMP - I
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Section 9: CALPUFF 5 SYKM real Sour
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Section 10: POSTPROCESSORS Table 10
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Section 10: POSTPROCESSORS 10.6 Out
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