1
|
flag_multi
|
run option
|
1 |
multi run |
| 2 |
multi run; climate sensitivity |
6
|
single
run with the same initialisation for every year |
| 7 |
multi run
with a list of control files for climate, soil,
management,stand initialisations, deposition, litter initialisation, CO2 flag |
8
|
multi run;
multi run with different data sets |
| 9 |
multi run with different data sets similar flag_multi = 8; allows simulation with divers climate scenarios (0 - 3K) and a set of its realisations |
| 10 |
multi run with different data sets similar flag_multi = 9; allows simulation with divers climate scenarios (RCP) and a set of its realisations |
| 2 |
site_nr |
number of runs |
integer |
with flag_multi = 1, 6, 8, 9, 10 |
| 3 |
*** |
simulation specifications |
comment line |
|
| 4 |
year |
number of simulation years |
integer |
|
| 5 |
time_b |
start year of simulation |
integer |
|
| 6 |
kpatchsize |
patchsize [m²] default = 200 |
real |
|
| 7 |
dz |
foliage layer thickness [cm] default = 50 |
real |
see 4C_description, Chapter 2.1;
no changes are recommended |
| 8 |
ns_pro |
Time step photosynthesis [d] default = 7 |
integer |
see 4C_description, Chapter 4.2;
no changes are recommended |
| 9 |
*** |
choice of model options |
comment line |
|
| 10 |
flag_mort |
mortality flag |
0 |
without mortality |
| 1 |
with stress mortality only; see 4C_description, Chapter 7.2 |
| 2 |
with stress and intrinsic mortality; see 4C_description, Chapter 7 |
11
|
flag_reg
|
regeneration flag
|
0 |
without regeneration |
| 1 |
with regeneration; see 4C_description, Chapter 8 |
| 2 |
with regeneration and weekly seedling growth |
| 3 |
generation of several cohorts at one time step |
| 10 |
planting of pine seedlings |
| 11 |
planting of beech seedlings |
| 12 |
planting of oak seedlings |
| 13 |
planting of spruce seedlings |
| 14 |
planting of birch seedlings |
15
|
planting of aspen seedlings
|
| 16 |
planting of Aleppo pine seedlings |
| 17 |
planting Douglas fir seedlings |
| 18 |
planting black locust seedlings |
| 20 |
planting of small trees in the first year given by data from
file *.pla |
30
|
regeneration according to data
from FORGRA (given by Vincent Kint)
|
| 12 |
flag_forska |
use FORSKA environmental factors and regeneration |
(default = 0) |
not in use, 0 has to be set |
| 13 |
flag_stand |
initialisation flag |
0 |
without Initialisation |
| 1 |
read data from *.ini |
| 2 |
generate *.ini from original stand data; see 4C_initialization_manual.pdf |
| 14 |
flag_sveg |
ground vegetation |
0 |
no ground vegetation |
| 1 |
initialisation of ground vegetation with fixed data set; no input is neccessary |
15
|
flag_mg
|
management flag
|
0 |
without management |
| 1 |
simple management routine |
| 2 |
new management routines
(thinnings) (not recommended) |
| 3 |
target based management,
adapted for applications in OakChain (using target stem numbers for thinning) |
| 33 |
target based management (using relative biomass reduction parameter) |
| 4 |
seeding routine, seeds once in simulation time |
| 5 |
thinning of dead trees, which are removed from stand (no litter
input) |
| 8 |
SRC management |
| 9 |
Austrian management |
| 10 |
disturbance management (Bavaria) |
| 16 |
flag_dis |
disturbance flag |
0 |
without disturbance |
| 1 |
with biotic disturbance (mistletoe, defoliator, stem, xylem, phloem or root disturber);
a management file must be available given with the appropriate flag_mg;
see 4C_description, Chapter 10 |
| 17 |
flag_light |
light algorithm number |
1 |
classical gap model approach,
see 4C_description, Chapter 3.5.1 |
| 2 |
cohorts with crown projection area, light is averaged after
each layer,
see 4C_description, Chapter 3.5.2 |
| 3 |
cohorts with crown projection area, light is absorbed per layer
and cohort,
see 4C_description, Chapter 3.5.3 |
| 4 |
cohorts with crown projection area, light is absorbed per layer
and cohort and modified by average yearly sun inclination,
see 4C_description, Chapter 3.5.4 |
| 18 |
flag_folhei |
foliage-height relationship |
0 |
old (linear) |
| 1 |
new (nonlinear),
see 4C_description, Chapter 4.4.2 |
| 19 |
flag_volfunc |
volume function |
0 |
old (two sapwood cones) |
| 1 |
new (sapwood cylinder below crown base and cone above),
see 4C_description, Chapter 4.4.3 |
| 20 |
flag_resp |
respiration flag |
0 |
tree respiration equals 0.52*NPP |
| 1 |
tree respiration modeled with organ specific respiration rates),
see 4C_description, Chapter 4.3 |
21
|
flag_limi
|
limitation flag (limitations of Photosynthesis)
|
0 |
no limitation |
| 1 |
only drought limitation),
see 4C_description, Chapter 4.2.3 |
| 2 |
only nitrogen limitation; fixed per species), see 4C_description, Chapter 4.2.4 |
| 3 |
like 2 and drought limitation |
6
|
nitrogen dynamic from mineralisation,
only nitrogen limitation;
daily, per cohort;
see 4C_description, Chapter 4.2.4, Eq. (4.19) |
7
|
nitrogen dynamic from mineralisation,
drought and nitrogen limitation; daily, per cohort; see 4C_description, Chapter 4.2.4, Eq. (4.19) |
8
|
only nitrogen limitation, age-dependent
|
9
|
drought and age-dependent nitrogen
limitation
|
| 10 |
drought and nitrogen limitation;
no N-limitation at 120 kg/ha anorganic N, under it decrease depending on N demand and N mineralisation;
see 4C_description, Chapter 4.2.4, Eq. (4.20) |
| 11 |
reduction of photosynthesis by ratio of cumulated N uptake and N demand of each species;
daily calculation;
see 4C_description, Chapter 4.2.4, Eq. (4.21) |
| 12 |
exponential reduction of photosynthesis by ratio of cumulated N uptake and N demand of each species;
daily calculation;
see 4C_description, Chapter 4.2.4, Eq. (4.23) |
| 13 |
reduction of photosynthesis by modified ratio of cumulated N uptake and N demand of each species;
daily calculation;
see 4C_description, Chapter 4.2.4, Eq. (4.22) |
| 14 |
N limitation like 13;
no drought limitation |
| 15 |
N limitation like 13;
for species Pinus sylvestris another approach is used;
see 4C_description, Chapter 4.2.4, Eq. (4.24) |
22
|
flag_decomp
|
choice of decomposition
model
|
0 |
uniform decomposition
model of all litter fractions (incl. stem wood and coarse roots) |
1
|
stem wood and coarse
root decay in a separate model with no direct N mineralisation,
input into the humus layer according to N release;
see 4C_description, Chapter 6.3.2 |
| 10 |
like 0; N uptake is controlled by N-supply of the cohorts;
see 4C_description, Chapter 6.3.5 |
| 11 |
like 1; N uptake is controlled by N-supply of the cohorts |
| 20 |
like 0; read litter input for selected years |
| 21 |
like 1; read litter input for selected years |
| 30 |
like 0; no litter input |
| 31 |
like 1; no litter input |
| 40 |
like 0; N uptake is controlled by C/N-ratio of non-heartwood |
| 41 |
like 1; N uptake is controlled by C/N-ratio of non-heartwood |
| 23 |
flag_sign |
root activity function flag |
0 |
constant sigman |
| 1 |
sigman varies with tree dimension |
| 24 |
flag_wred |
soil water uptake flag |
1 |
function with uptake inhibition near wilting point and field
capacity;
see 4C_description, Chapter 6.1.3, case a) |
| 2 |
uptake restrict to 4% |
| 3 |
reduction along a profile |
| 4 |
specific reduction function for Beerenbusch |
| 5 |
no reduction |
| 6 |
uptake restrict to 50% |
| 7 |
uptake restrict to 25% |
| 10 |
function with uptake exponential inhibition near wilting point and field capacity;
see 4C_description, Chapter 6.1.3, case b) |
| 11 |
case for Mistletoe, function after van Wijk, 2000 with a very strong reduction in water availability |
| 25 |
flag_wurz |
root distribution flag |
0 |
equally distributed over all layers |
| 1 |
root profile: Jackson approach;
see 4C_description, Chapter2.3.1, case b) |
| 2 |
input of root profile after request; unchanged during the simulation
time |
| 7 |
Jackson approach with fixed root depth given from soil data |
26
|
flag_cond
|
heat conductance flag
|
0 |
thermal conductivity: de Vries-approach; soil surface
temperature equals temperature of 1. layer, physical soil parameters wil be recalculated depending on humus content;
see 4C_description, Chapter 6.2.2, case b) |
1
|
thermal conductivity:
Neusypina-approach; soil surface temperature equals temperature
of 1. layer;
see 4C_description, Chapter 6.2.2, case a) |
| 3 |
thermal conductivity:
Campbell approach; soil surface
temperature equals temperature of 1. layer, physical soil parameters wil be recalculated depending on humus content;
see 4C_description, Chapter 6.2.2, case e) |
10
|
thermal conductivity:
de Vries-approach; real soil surface temperature (additional
to the soil profile), physical soil parameters wil be recalculated depending on humus content |
| 11 |
thermal conductivity:
Neusypina-approach; real soil surface temperature (additional
to the soil profile) |
| 13 |
thermal conductivity:
Campbell approach; real soil surface temperature (additional
to the soil profile), physical soil parameters wil be recalculated depending on humus content |
| 20 |
thermal conductivity:
de Vries-approach; reading soil surface temperature after request, physical soil parameters wil be recalculated depending on humus content |
| 21 |
thermal conductivity:
Neusypina-approach; reading soil surface temperature after
request |
| 23 |
thermal conductivity:
Campbell approach; reading soil surface temperature after
request, physical soil parameters wil be recalculated depending on humus content |
| 30 |
thermal conductivity:
de Vries-approach; real soil surface temperature (additional
to the soil profile), daily correction factor and damping coefficient constant 1, physical soil parameters wil be recalculated depending on humus content |
| 31 |
thermal conductivity:
Neusypina-approach; real soil surface temperature (additional
to the soil profile), daily correction factor and damping coefficient constant 1 |
| 33 |
thermal conductivity:
Campbell approach; real soil surface temperature (additional
to the soil profile), daily correction factor and damping coefficient constant 1, physical soil parameters wil be recalculated depending on humus content |
| 40 |
thermal conductivity:
de Vries-approach; real soil surface temperature (additional
to the soil profile), no recalculation of physical soil parameters depending on humus content |
| 41 |
thermal conductivity:
Neusypina-approach; real soil surface temperature (additional
to the soil profile), no recalculation of physical soil parameters |
| 43 |
thermal conductivity:
Campbell approach; real soil surface temperature (additional
to the soil profile), no recalculation of physical soil parameters |
27
|
flag_int
|
interception flag
|
0 |
total interception of canopy and
ground vegetation (with total crown storage capacity) |
| 1 |
interception for each cohort
(with storage capacity in each crown layer and with distribution
of precipitation over all canopy layers) |
| 2 |
interception for each cohort
(with storage capacity for each cohort); precipitation distributed
according to foliage |
| 3 |
pine interception from Anders (storage
capacity = 2.9 mm) |
4
|
fit
for Level II Brandenburg, pine (20% of precipitation) |
5
|
30%
of precipitation (for spruce); faster evaporation |
| 6 |
no interception |
| 10xx |
like 0; reduction of throughfall to xx % |
| 11xx |
like 1; reduction of throughfall to xx % |
| 12xx |
like 2; reduction of throughfall to xx % |
| 16xx |
like 6; reduction of throughfall to xx % |
28
|
flag_eva
|
evapotranspiration flag
|
0 |
Turc / Ivanov; calculation of transpiration demand after deduction of soil evaporation and interception with BIOME3 approach |
| 1 |
Priestley / Taylor |
| 2 |
Priestley / Taylor for each cohort |
| 3 |
Penman / Monteith; not recommended for long simulation periods (greater than 40 years) |
| 4 |
Penman / Monteith for each cohort; not recommended for long simulation periods (greater than 40 years) |
| 5 |
Haude |
| 6 |
Turc / Ivanov; calculation of transpiration demand without consideration of soil evaporation and interception with BIOME3 approach |
| 7 |
Turc / Ivanov; transpiration demand from potential evapotranspiration after deduction of soil evaporation and interception |
29
|
flag_CO2
|
CO2 flag
|
0 |
constant atmospheric mixing ratio (350 ppm) |
| 1xx (xx = as choice detailed below) |
increasing atmospheric mixing ratio as historic increase |
2xx (xx = as choice detailed
below)
|
step change in the middle of the
simulation period |
xx = 01
|
Kohlmaier function |
| xx = 02 |
LTEEF scenario |
| xx = 03 |
Mauna Loa series |
xx = 10
|
IPCC IS92a after Bern CC model,
reference |
xx = 11
|
IPCC SRES A1FI after Bern CC model,
reference |
xx = 12
|
IPCC SRES A2 after Bern CC model,
reference |
xx = 13
|
IPCC SRES B1 after Bern CC model,
reference |
| xx = 14 |
IPCC B2 after Bern CC model, reference |
| xx = 15 |
IPCC A1B after Bern CC model, reference |
| xx = 16 |
IPCC A1p after Bern CC model,
reference |
| xx = 17 |
RCP8.5, final release, 26 Nov. 2009 |
| xx = 18 |
RCP2.6, final release, 26 Nov. 2009 |
| xx = 19 |
RCP4.5, final release, 26 Nov. 2009 |
| xx = 20 |
RCP6.0, final release, 26 Nov. 2009 |
| xx = 31 |
RCP2.6, 1765-2300, PROFOUND-DB |
| xx = 32 |
RCP6.0, 1765-2300, PROFOUND-DB |
| xx = 33 |
1765 - 2005 historical data (PROFOUND-DB), time>2005 CO2 = 378.81 ppm |
| yyy |
setting of constant atmospheric mixing ratio yyy ppm with yyy > 250 ppm (integer) |
| 199 |
special function implemented (Hyytiälä) |
30
|
flag_sort
|
assortment
|
0 |
all assortments |
| 1 |
without stems (Stammholz) |
| 2 |
only LAS with 3m + industrial
+ fuel wood |
| 3 |
only LAS with 4m + industrial +
fuel wood |
31
|
flag_wpm
|
wood product model
|
0 |
(default = 0)
if 1: wood product model (WPM) is called with output |
| 2 |
Socio- Economic Analyses (SEA)
called with output |
| 3 |
SEA and WPM called with output |
32
|
flag_stat
|
statistic flag
|
0 |
no analysis |
1
|
comparison with measurements and
statistical analysis |
2
|
additional to 1 output of the
triples of measurement , simulation value and residual |
| 33 |
*** |
output specifications |
comment line |
|
| 34 |
time_out |
Yearly output flag |
0 |
no |
| n (n=1,2,3,...) |
yes; output every n years |
| -1 |
output of control file and compressed
files at start and end |
| -2 |
output of compressed file at end
without header (only useful with simenv-version) |
35
|
|
Selection of yearly output files |
string |
selection
of any yearly output files; each name in a new line; ending
with end (always
necessary) |
| 36 |
flag_dayout |
Daily output flag |
0 |
no |
| 1 |
yes |
| 37 |
|
Selection of daily output files |
string |
selection
of any daily output files; each name in a new line; ending
with end (always
necessary) |
| 38 |
flag_cohout |
cohort output flag |
0 |
no |
| 1 |
yes |
| 2 |
yes with additinal output of special files from the allocation, the NPP, and the light module |
39
|
|
Selection of cohort output file |
string |
selection
of any cohort output files; each name in a new line; ending
with end (always
necessary) |
40
|
flag_sum
|
summation output flag
|
0 |
|
| 1 |
daily output |
| 2 |
output with time step of photosynthesis |
| 3 |
monthly |
4
|
yearly |
| 41 |
*** |
input data |
comment line |
|
| 42 |
specfile |
species parameter file (species.par) |
string |
|
| 43 |
site_name |
name of output-files |
string |
identifier (first part of the name
of all output files of this run) |
44
|
climfile
|
name of climate data file
|
string |
|
| 45 |
sitefile |
name of soil data file (*.sop) |
string |
|
| 46 |
valfile |
dummy or identification of soil profile resp. |
string |
line is always mandatory; in case of a sitefile with multiple soil profiles the identification of the soil profile is given here |
| 47 |
treefile |
name of initialisation file of stand (*.ini) |
string |
|
| 48 |
standid |
stand identifier |
integer |
stand identifier for use of multi initialisation file; be skipped
with 999
in case of single initialisation file |
| 49 |
manfile |
management file |
string |
|
50
|
depofile
|
name
of deposition data file (*.dep) |
string |
in case of dummy file or file not
found: all deposition data set to zero
|
51
|
redfile
|
name
of RedN file (*.red) |
string |
values
of RedN (model parameter - N reduction of photosynthesis);
in case of dummy file or file not found: internal calculation
of RedN |
| 52 |
litfile |
|
string |
data of litter fraction initialisation;
in case of dummy file or file not found: internal
initialisation of litter fractions
|
| 53 |
*** |
run number |
comment line |
!!! all following lines only necessary with flag_multi = 1 and number of runs > 1!!! |
| 54 |
|
|
(integer, flag_name) |
change of any flags
(in pairs of value and flag_name) ending
with a certain line (value < 0, flag_name = end); this last
line is always necessary |
| 55 |
specfile |
species parameter file (species.par) |
string |
|
| 56 |
site_name |
name of output-files |
string |
|
57
|
climfile |
name of climate data file |
string |
|
| 58 |
sitefile |
name of soil data file (*.sop) |
string |
|
| 59 |
valfile |
dummy or identification of soil profile resp. |
string |
line is always mandatory; in case of a sitefile with multiple soil profiles the identification of the soil profile is given here |
| 60 |
treefile |
name of initialisation file of stand (*.ini) |
string |
|
| 61 |
standid |
stand identifier |
integer |
stand identifier for use of multi initialisation file; be skipped
in case of single initialisation file |
| 62 |
manfile |
management file |
string |
|
| 63 |
depofile |
name of deposition data file (*.dep) |
string |
|
| 64 |
redfile |
name of RedN file (*.red) |
string |
|
65
|
litfile |
name of
litter initialisation file (*.lit) |
string |
|
