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Optimal calibration of evaporation models against Penman-Monteith equation

Abstract

We present an approach for the calibration of simplified evaporation model parameters based on the optimization of parameters against the most complex model for evaporation estimation, i.e., the Penman-Monteith equation. This model computes the evaporation from several input quantities, such as air temperature, wind speed, heat storage, net radiation etc. However, sometimes all these values are not available, therefore we must use simplified models. Our interest in free water surface evaporation is given by the need for ongoing hydric reclamation of the former LeZaky-Most quarry, i.e., the ongoing restoration of the land that has been mined to a natural and economically usable state. For emerging pit lakes, the prediction of evaporation and the level of water plays a crucial role. We examine the methodology on several popular models and standard statistical measures. The presented approach can be applied in a general model calibration process subject to any theoretical or measured evaporation.

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Optimal calibration of evaporation models against Penman-Monteith equation

Author: Dlouhá, Dagmar
Publisher: MDPI
Year: 2021
DOI: 10.3390/w13111484
Source: https://dspace.vsb.cz/bitstreams/005c2c2a-e261-4e5e-8229-c1bf64dc1d7b/download
wa e
A icle
Op imal Calib a ion o E apo a ion Models agains
Penman–Mon ei h Equa ion
Dagma Dlouhá , Vik o Dubo ský * and Lukáš Pospíšil


Ci a ion: Dlouhá, D.; Dubo ský, V.;
Pospíšil, L. Op imal Calib a ion o
E apo a ion Models agains
Penman–Mon ei h Equa ion. Wa e
2021,13, 1484. h ps://doi.o g/
10.3390/w13111484
Academic Edi o : Guido D’U so
Recei ed: 26 Feb ua y 2021
Accep ed: 24 May 2021
Published: 25 May 2021
Publishe ’s No e: MDPI s ays neu al
wi h ega d o ju isdic ional claims in
published maps and ins i u ional a il-
ia ions.
Copy igh : © 2021 by he au ho s.
Licensee MDPI, Basel, Swi ze land.
This a icle is an open access a icle
dis ibu ed unde he e ms and
condi ions o he C ea i e Commons
A ibu ion (CC BY) license (h ps://
c ea i ecommons.o g/licenses/by/
4.0/).
Depa men o Ma hema ics, Facul y o Ci il Enginee ing, VSB-TU Os a a, Lud íka Podéš ˇe 1875/17,
708 00 Os a a, Czech Republic; dagma [email p o ec ed] (D.D.); [email p o ec ed] (L.P.)
*Co espondence: ik o [email p o ec ed]
Abs ac :
We p esen an app oach o he calib a ion o simpli ied e apo a ion model pa ame e s
based on he op imiza ion o pa ame e s agains he mos complex model o e apo a ion es ima ion,
i.e., he Penman–Mon ei h equa ion. This model compu es he e apo a ion om se e al inpu
quan i ies, such as ai empe a u e, wind speed, hea s o age, ne adia ion e c. Howe e , some imes
all hese alues a e no a ailable, he e o e we mus use simpli ied models. Ou in e es in ee wa e
su ace e apo a ion is gi en by he need o ongoing hyd ic eclama ion o he o me Ležáky–Mos
qua y, i.e., he ongoing es o a ion o he land ha has been mined o a na u al and economically
usable s a e. Fo eme ging pi lakes, he p edic ion o e apo a ion and he le el o wa e plays
a c ucial ole. We examine he me hodology on se e al popula models and s anda d s a is ical
measu es. The p esen ed app oach can be applied in a gene al model calib a ion p ocess subjec o
any heo e ical o measu ed e apo a ion.
Keywo ds:
model calib a ion; e apo a ion; Penman–Mon ei h equa ion; op imiza ion; c oss- alida ion
1. In oduc ion
E apo a ion and e apo anspi a ion play a c ucial ole in wa e managemen in a
wide ange o human ac i i ies and hus he e is a s ong need o accu a e es ima es.
This need leads o a conside able numbe o pape s and s udies ha a e o e ing new
me hods o such es ima es o compa ison o me hods al eady used in hyd ologic engi-
nee ing applica ions. The esul s o es ima ion could be compa ed wi h e e ence e apo a-
ion/e apo anspi a ion calcula ed by FAO Penman–Mon ei h equa ion
EFAO
, which is
ecommended as he s anda d me hod [
1
,
2
]. This equa ion is conside ed o be an e alon
o which he esul s o he o he me hods can be ela ed and compa ed. The pape s
dealing wi h e apo a ion o e apo anspi a ion p esen he compa ison o he FAO Penman–
Mon ei h me hod esul s o o he me hods p oposing he ela ions be ween inpu da a less
complica ed and compu a ionally less demanding. Fo ins ance, such a p ocedu e was
pe o med in he s udy [
3
] o ind he bes es ima ion o wa e los om a co e ed ese oi .
In [
4
] i is s a ed ha
EFAO
p o ides good ag eemen wi h e apo a ion measu ed on
120ha
dam. In [
5
],
EFAO
is used no only as a e e ence me hod and bu also a ounda ion o new
nume ical models de i ed by mul iple linea eg ession and design o expe imen me hod,
ollowed by he simpli ied me hodology o he quan i ica ion o he e apo a ion a e o
a basin wi h a pho o ol aic sys em. Simila ly, he possibili y o educ ion o Lake Nasse
e apo a ion using a loa ing pho o ol aic sys em is desc ibed in [
6
]. Ou esea ch is no
ocused only on he a ea o Lake Mos , bu also on pi lakes ha a e only planned, he e o e
i is impossible o use limnological and ba hyme ic da a, such as empe a u e p o ile o
wa e dep h. Such a si ua ion is conside ed in [
7
], whe e au ho s used he
EFAO
o he
compu a ion o he open wa e e apo a ion es ima ion.
FAO Penman–Mon ei h me hod is cha ac e ized by a s ong likelihood o co ec ly
p edic ing e apo anspi a ion in a wide ange o loca ions and clima es wi h di e ing
Wa e 2021,13, 1484. h ps://doi.o g/10.3390/w13111484 h ps://www.mdpi.com/jou nal/wa e
Wa e 2021,13, 1484 2 o 23
local condi ions, e.g., sola adia ion, sunshine du a ion, wind speed, ai humidi y, ai
empe a u e [8–10].
Ou in e es in ee wa e su ace e apo a ion is gi en by he need o ongoing hyd ic
ecul i a ion o he o me Ležáky–Mos qua y (Czech Republic), i.e., Lake Mos , as well
as ano he planned hyd ic ecul i a ion in he egion. One o he key componen s o hyd ic
eclama ion planning is he secu i iza ion o long- e m sus ainabili y, which is based on he
capabili y o keeping he s able le el o a dimension o he inal wa e le el.
Hyd ic ecul i a ion was p oposed o be he bes way o deal wi h he esidual o open-
cu coal mines in he no h-wes e n egion o he Czech Republic. A e he mine is closed,
he oid could be illed by su ace wa e uno and g oundwa e . In he case ha hese
esou ces a e no s ong enough, he pi lake has o be illed a i icially and ha is he case o
he o me Mos -Ležáky mine and Lake Mos . The le el o he new lake has been p oposed
o be s able wi h a wa e le el a
199m
abo e sea le el assuming he abula ed alues o
p ecipi a ion and e apo a ion be ween
500mm
and
600mm
annually [
11
]. Howe e , his
assump ion ails o be ue [12].
The e olu ion o a i icial pi lakes is a ec ed by a wide ange o chemical, physical,
and namely hyd ological p ocesses such as sa u a ion o he coas al lines, leakage h ough
he bo om, and ee su ace e apo a ion. As he lake bo om was sealed be o e illing,
e apo a ion was supposed o be he main cause o he obse ed wa e loss.
Toge he wi h he p ecipi a ion, he open wa e e apo a ion and ege a ion e apo an-
spi a ion o m he main componen s o he wa e cycle in na u e, and i is said ha he
e apo a ion o e he land su ace amoun s o abou wo hi ds o he a e age p ecipi a ion,
see [
13
]. Howe e , hese es ima es di e om loca ion o loca ion and e apo a ion mea-
su emen o calcula ion p ocedu es a e complica ed and bu dened wi h a high deg ee o
unce ain y. This happens due o he complexi y o e apo a ion as a physical phenomenon
and se e al ac o s ha a ec his p ocess. The a e o e apo a ion could be measu ed o
calcula ed, howe e , because o he simpli ica ion o he e apo a ion p ocess desc ip ion,
bo h measu emen and compu a ional me hods p o ide only he app oxima ion o ac-
ual e apo a ion. Fo u he discussion abou he his o ical de elopmen o e apo a ion
and e apo anspi a ion, see [
14
] men ioning 166 models and equa ions ob ained du ing
he las h ee cen u ies. The desc ip ion and cha ac e iza ion o all physical p ocesses
a ec ing e apo a ion could be ound in a classical book by B u sae [
15
], o Maidmen [
16
]
( Shu lewo h’s chap e ).
Fo compu a ional me hods, he e a e wo ways o handle e apo a ion, desc ibed as
mass ans e o ene gy budge me hods, see [
13
]. Fu he mo e, he models could be iewed
as empe a u e-based, adia ion-based,mass ans e -based, and combined me hods based on he
inpu s used o calcula e he a e o e apo a ion, o addi ional de ails see [2,16–18].
Addi ionally, wi hin each g oup, he e a e se e al equa ions, which a e widely ci ed
in he echnical li e a u e. Du ing he s udy o a ious e apo a ion models in he li e a u e,
one can obse e se e al di icul ies. One o he main di icul ies is he inconsis encies in he
used physical uni s. Fo ins ance, acco ding o he ime and place o publica ion o a icles
o books, he same equa ion can be encoun e ed wi h he p essu e gi en in
kPa
,
mba
,
To
o millime e s o me cu y column. This a iabili y o uni s can cause di e en shapes o he
same equa ions in di e en sou ces, e en when he same uni s a e used. Fu he mo e,
di e en ypes o me hods equi e di e en ype o da a. Howe e , in p ac ical applica ions,
we a e no able o measu e all ypes o inpu pa ame e s, he e o e he choice o he model
depends no only on he modelling quali y bu mainly on he abili y o measu e he equi ed
inpu physical quan i ies.
This is one o he main easons why he de elopmen o new simpli ied models is s ill
ac i e. The FAO equa ion is a solid s anda d, bu some imes oo complex o be handled in
p ac ice. Fo ins ance, in he a icle [
19
], eigh een empe a u e-, adia ion-, mass ans e -based
and combined me hods a e s udied unde he condi ion o clima ic change in Ge many. The
FAO equa ion is compa ed wi h 31 me hods unde he humid clima e condi ion in I an
Wa e 2021,13, 1484 3 o 23
in he pape [
20
]. In [
21
], i e empe a u e-based me hods and h ee adia ion me hods
a e conside ed.
In his pape , we a e looking o he simpli ica ion o he FAO equa ion in e ms o
he numbe o inpu quan i ies. Ou goal is o use less complex models o model he
e apo a ion in he a ea o Lake Mos by calib a ing he pa ame e s o he models in he
i ing op imiza ion p ocess agains he e apo a ion es ima ion by FAO using selec ed
s a is ical measu es. The mo i a ion came om he lack o measu ing de ices in he di ec
a ea o he lake. In his pape , we conside models which equi e only he ai empe a u e,
wind speed, and ela i e humidi y. Besides he Lake Mos , we a e in e es ed also in he
planned pi lakes. The e o e, he ypes o models a e limi ed o hose which equi es only
hese basic me eo ological da a. In his case, i is no possible o measu e, o ins ance, he
empe a u e o he wa e .
The pe o mance o he conside ed me hods can be e alua ed s a is ically, and se e al
s a is ical measu es could be used. The mos commonly used a e he Roo Mean Squa e
E o (RMSE), Mean absolu e e o (MAE), and he Mean Bias E o (MBE), see, o in-
s ance, [
22
]. Addi ionally, he RMSE and MBE could be combined o calcula e he so-called
-s a is ic es , which exp esses he le el o con idence be ween he models, see [
23
]. A
qui e unusual measu e could be ound in [
24
], i is mean a io
MR
, which is compu ed as
he a e age o a ios be ween he p edic ed and obse ed alues. Ano he way o compa e
wo gi en models is o compu e Pea son’s co ela ion coe icien (PCC)
o o compu e
R2
coe icien o de e mina ion. These wo measu es a e closely connec ed since R2is squa e
o
. The simples measu e o he p edic ion quali y is he pe cen age exp ession o he
di e ence be ween models. This is a s a is ical measu e ha is well known as pe cen
bias (PBIAS). The las class o s a is ical measu es ha desc ibe he co espondence o
obse ed and simula ed da a a e ag eemen indices, such as Nash–Su cli e e iciency (NSE)
and Willmo ’s ag eemen index. These a e used, o example, in [
21
,
25
,
26
]. Fo u he
discussion o s a is ical model e alua ions, see [
27
]. In his pape , we compa e se e al se-
lec ed s a is ical measu es, namely
NSE
,
RMSE
,
MAE
, and
PBIAS
. Howe e , we suppose
ha ou me hodology can be applied o any chosen dis ance unc ion. The applicabili y
depends on he abili y o sol e he co esponding eg ession p oblem.
The choice o empe a u e-based me hods in he case o he Lake Mos s udy is no due
o he cu en lack o me eo ological da a since Kopis y me eos a ion is loca ed only
1km
om he lake. The simpli ica ion o he equa ion is mo i a ed by he u he planned hyd ic
ecul i a ions in he egion. Planned pi lakes a e mo e dis an om Kopis y and he e o e
he me eo ological da a p o ided o he models om Kopis y would no be su icien . The
da a p o ided o he models on new lakes will be measu ed di ec ly on he a ea o new
lakes. In he case o Lake Mos , we can iden i y he app op ia e simpli ied model because
o ad an ageous loca ion o Kopis y wi h espec o Lake Mos . The e o e, we a e in e es ed
in he iden i ica ion o he simples sui able model wi h he low demand on inpu da a.
The cons uc ion o he new wea he s a ion in he a ea close o he new lake does no
make any sense om he inancial poin o iew (because o he p esence o Kopis y wea he
s a ion). On he o he hand, o p o ide be e es ima ions, we should measu e he inpu
da a as close as possible o he a ea o in e es . The measu emen o , o ins ance, he
empe a u e is ela i ely cheap. The only ques ion is i he empe a u e is a su icien
amoun o inpu me eo ological da a o p o iding a su icien es ima ion. The accu acy o
he wa e loss due o e apo a ion is c ucial o hose planned a i icial lakes. To p o ide he
bes possible es ima e, he expe iences om he Lake Mos will be used. In his pape , we
compa e se e al simpli ied models wi h espec o di e en s a is ical measu es, namely
NSE,RMSE,MAE, and PBIAS.
Addi ionally, o a oid he o e i ing o he calib a ed model, we adop he c oss-
alida ion me hodology [
28
]. We andomly spli he da a in o calib a ion and alida ion
pa s. The pa ame e s o he model a e op imized on he calib a ion se and es ed on he
alida ion pa . Resul s om he alida ion pa a e u he analyzed and he bes model is
chosen conce ning esul s om all c oss- alida ion spli ings.
Wa e 2021,13, 1484 4 o 23
The pape is o ganized as ollows. Sec ion 2.4 in oduces he me hods and ma e ials
used in ou compu a ion. To be mo e speci ic, we s a wi h he p esen a ion o he Lake
Mos in Sec ion 2.1, and he da a p o ided o he models in Sec ion 2.2. A e wa ds, we
e iew he FAO equa ion in Sec ion 2.3 and he simpli ied models in Sec ion 2.4. Du ing
he calib a ion p ocess, we use he s a is ical measu es p esen ed in Sec ion 2.5. The whole
me hodology is implemen ed in R p og amming language, see Sec ion 2.6 o de ails. This
sec ion also includes he desc ip ion o he used c oss- alida ion p ocess. The esul s a e
p esen ed in Sec ion 3and discussed in Sec ion 4. Finally, Sec ion 5concludes he pape .
The pape can be conside ed o be an ex ension o ou p e iously published wo k [
29
].
2. Ma e ials and Me hods
2.1. S udy A ea
The Lake Mos is si ua ed in he No h o he Czech Republic nea he ci y o Mos
50
◦
C310
0
N, 13
◦
C360
0
E, see Figu e 1. I was c ea ed by he hyd ic ecul i a ion o he
Mos –Ležáky qua y in he cen al pa o he No h Bohemian b own coal basin. The o me
mine hea ily a ec ed he a ea o
1254ha
and he pi lake, as a pa o i s e i aliza ion, was
planned o ha e a su ace a ea o abou
300ha
. The p ojec o he e i aliza ion is secu ed
by he s a e en e p ise Pali o ý kombiná Ús í (PKU) [30].
Figu e 1. Lake Mos and he su ounding a ea (sou ce: www.pku.cz, Google Ea h).
Be o e he looding, i was necessa y o ake echnical a angemen s such as sealing he
bo om o he u u e lake, cons uc ion o an unde g ound sealing wall, and s eng hening
he sho eline. All hese a angemen s allow iewing he Lake Mos as a closed sys em
wi hou na u al in low o ou low. Due o he absen na u al in low, he esidual pi o
he lake was illed h ough an a i icial eede du ing he pe iod om 2008 o 2014. In he
inal phase o lake illing, i.e., in he yea 2014, he su ace le el ose om
197.74m
o he
equi ed le el o 199m abo e sea le el.
A e inishing he illing p ocess, Lake Mos has an ac ual su ace a ea o
309.4ha
,
a coas al line leng h o
8.9km
, a o al wa e olume o
70.5millionm3
, and a maximum
dep h o
75m
. Th oughou he illing o he lake, bo h ope a ional and basic me eo ological
da a we e moni o ed. The ope a ional da a con ain da a on he achie ed al i ude o he
lake le el, i s su ace a ea, and especially on he olume o wa e admi ed. The illing o
he lake has been inished in 2014 achie ing he equi ed su ace le el o 199m.
Wa e 2021,13, 1484 5 o 23
2.2. Da a and Da a Sou ces
In ou esea ch, we a e using he me eo ological da a collec ed du ing he yea s 2015–
2019. The collec ion includes all da a necessa y o he calcula ion o he Penman–Mon ei h
equa ion (see Sec ion 2.3). These me eo ological measu emen s we e pe o med a he
Kopis y wea he s a ion si ua ed app oxima ely
1km
om he lake. The s a ion is ope a ed
by CHMI—Czech Hyd ome eo ological Ins i u e and he da a a e eco ded a en-minu e
in e als. The da ase ob ained om CHMI was s a is ically p ocessed o be used in he
equa ions o model he e apo a ion. We p esen he da a basic s a is ics in Figu e 2. In
Kopis y wea he s a ion, he wind speed is measu ed a
10m
abo e he g ound o a oid
he in luence o he g ound. The ai empe a u e and humidi y a e measu ed a
2m
abo e
he g ound.
We also included p ecipi a ion equency o he demons a ion o he hyd ological
balance in he a ea o in e es . In compa ison wi h he a e age empe a u e and p ecip-
i a ion in he Czech Republic, he a ea o he planned hyd ic eclama ion is in he a ea
wi h he empe a u e s ongly abo e he a e age and p ecipi a ion s ongly below no mal
p ecipi a ion, and wi h he numbe o hou s o sunshine below he ypical alue in he
Czech Republic [11].
Figu e 2.
The basic s a is ics o he daily measu emen s pe o med a he Kopis y wea he s a ion du ing he yea s 2015–2019:
a e age day empe a u e
Ta
, a mosphe ic p essu e
P
, dayligh hou s pe day
n
, ela i e humidi y
RH
, wind speed
u2
, and
p ecipi a ion p . These da a a e used in he equa ions o modelling he e apo a ion.
2.3. Penman–Mon ei h Equa ion
The EFAO equa ion is o he o m
EFAO =0.408 ∆(Rn−G)+γ900
Ta+273 u2(es−ea)
∆+γ(1+0.34 u2). (1)
Please see Sec ion Abb e ia ions a he end o his pape o he desc ip ion and
physical uni s o he used a iables.
Acco ding o Linac e pape [
31
] o daily es ima es o he e apo a ion a e o ee wa e
le el, he e m Gcan be neglec ed, i.e., we se G=0.

Wa e 2021,13, 1484 6 o 23
The e m
(es−ea)
in
[kPa]
, is he di e ence o sa u a ion apo p essu e and ac ual
apo p essu e. The alues esand eaa e gi en by
es=1
20.6108 e 17.27 Tmax
Tmax+237.3 +0.6108 e 17.27 Tmin
Tmin+237.3 ,ea=RH
100 es. (2)
The psych ome ic cons an
γ
depends on he a mosphe ic p essu e
P
in
[kPa]
and
on abo e-men ioned cons an s
Cp=1013Jkg−1°C−1
,
λ=2.45MJkg−1
and
ε=
0.622
[−]
,
wi h
ε
being a io molecula weigh o wa e apo o d y ai . To compu e i s alue, he
ollowing o mula is used
γ=CpP
ε λ =0.665 ×10−3P. (3)
Using his o mula, he compu ed alue o
γ
depends only on one measu ed quan i y
and ha is a mosphe ic p essu e Pand is gi en in kPa°C−1.
The slope
∆
desc ibes he ela ionship be ween sa u a ion apo p essu e and empe -
a u e. Fo a gi en empe a u e Ta, he co esponding ∆is gi en by
∆=
40980.6108e
17.27 Ta
Ta+237.3 
(Ta+237.3)2. (4)
The esul ing uni o ∆is kPa °C−1.
The ne adia ion a he su ace
Rn
in
hMJm−2day−1i
is, by [
1
], gi en as he di e ence
incoming ne sho wa e adia ion Rns and ou going ne long wa e adia ion Rnl, i.e.,
Rn=Rns −Rnl.
To e alua e
Rnl
, he knowledge o sola adia ion
Rs
and global ex a e es ial adia ion,
Rais equi ed.
Ex a e es ial adia ion is he amoun o adia ion inciden on a uni o he ho izon al
su ace a he ou e bounda y o he a mosphe e. Fo places o simila la i ude, i is
app oxima ely he same, changing only du ing he yea . The e is no in luence o cloud
u bidi y o ai pollu ion o e he Ea h’s a mosphe e, and he e o e, he dose o sola
ene gy is he highes a any gi en ime. In addi ion o he sola cons an , he angle o
incidence o he sun’s ays a a gi en loca ion o he a mosphe e bounda y mus also be
aken in o accoun . The e o e, he alue o
Ra
is exp essed depending on hese quan i ies as
Ra=24 ×60
πGsc d (ωssin ϕsin δ+sin ωscos ϕcos δ). (5)
The e ms included in Equa ion (5) a e
Gsc =0.082 MJ m−2min−1, global sola cons an ,
d =1+0.33 cos 2π
365 JD, Ea h-Sun ela i e dis ance [−],
δ=0.409 sin 2π
365 JD −1.39, sola declina ion [ ad],
ϕla i ude o he si e o in e es [ ad],
ωs=a ccos (− an ϕ an δ), sunse hou angle [ ad],
JD numbe o Julian day.
Wa e 2021,13, 1484 7 o 23
The e ms Rsand Rns could be compu ed by
Rs=as+bsn
NRa, (6)
Rns =(1−α)Rs, (7)
whe e
as
,
bs
a e Angs öm coe icien s,
n[h]
and
N[h]
a e ac ual and maximum possible du a-
ion o dayligh , espec i ely. Finally, αdeno es albedo, i.e., he coe icien o e lec ion.
As he Angs öm coe icien s a e no calcula ed based on he ac ual sola adia ion mea-
su emen s he e, he FAO pape [
1
] ecommenda ion
as=
0.25 and
bs=
0.5 in Equa ion
(6)
is used. Fu he mo e, he ee wa e su ace albedo is se as α=0.08 based on [1].
The maximum dayligh du a ion Nis compu ed as
N=24
πωs. (8)
To de e mine ne longwa e adia ion Rnl, he ollowing o mula is used
Rnl =σ (Tmax +273.16)4+(Tmin +273.16)4
2! 0.34−0.14√ea!1.35 Rs
Rso −0.35. (9)
The abo e o mula
(9)
uses he S e an-Bol zmann cons an
σ=4.903 ×10−9MJK−4m−2day−1
and
Rso
in
hMJm−2day−1i
, which is he clea -sky
adia ion.
The alue o he clea -sky adia ion Rso is calcula ed as
Rso =0.75 +2×10−5zRa,
whe e zis he si e al i ude in [m]abo e he sea le el.
Howe e , despi e i s complexi y o he FAO Penman–Mon ei h Equa ion
(1)
, i is
no possible o conside
EFAO
esul s o be accu a e, since he numbe o inpu da a o
be measu ed o calcula ed by empi ical o mulae based on measu ed inpu da a. Such
an es ima ion p ocess is a ec ed by measu emen and calcula ion e o s. Fo example,
in [
32
,
33
], one could ind sensi i i y analysis o he FAO Penman–Mon ei h equa ion in
di e en clima e condi ions.
I should be poin ed ou ha Equa ion
(1)
was de i ed as a me hod o de e mine he
e e ence a e o e apo anspi a ion, i.e., he e e ence a e o e apo a ion om g owing plan s
wi h he cha ac e is ics o hypo he ical e e ence c ops such as heigh ,ae odynamic esis ance o
hei su ace, and albedo. Fo eal c ops, he a e o e apo anspi a ion is de e mined om
EFAO by mul iplying he c op- ela ed coe icien Kc
Ec op =KcEFAO.
Wi h he p ope coe icien , he
EFAO
o mula could be used o es ima e open wa e
e apo a ion. The alues o coe icien
Kc
, i.e.,
Kc,mid
and
Kc,end
o mid and end season
espec i ely a e abula ed in [
1
]. Speci ically,
Kc,mid =Kc,end =
1.05 o shallow lakes, i.e., o
hose wi h a dep h o up o
2m
. Fo deep lakes, i.e., wi h a dep h exceeding
5m
, he alues
Kc,mid =
0.65 and
Kc,end =
1.25 a e indica ed. The e o e, i should be bo ne in mind ha
(especially in he case o deep lakes) he esul o
EFAO
could lead o he unde es ima ion
o up o 35% o he o e es ima ion up o 25% du ing he season.
Since ou esea ch is no ocused only on he a ea o Lake Mos , bu also on lakes
ha a e only planned and does no exis a p esen , i is impossible o use limnological
and ba hyme ic da a, such as empe a u e p o ile o wa e dep h. This leads us o he
conside a ions o he a icle [
7
], which s a es ha in he case o missing limnological da a,
he lake coe icien
Kc=
1 can be selec ed and
EFAO
esul i sel could be conside ed o be
Wa e 2021,13, 1484 8 o 23
an open wa e e apo a ion es ima e. Hence, in all ou calib a ion and alida ion p ocesses,
he equa ion EFAO se es us as an e alon and all ou esul s a e compa ed agains i .
2.4. E apo a ion Es ima ion Me hods
Since he FAO Penman–Mon ei h equa ion
EFAO
(see
(1)
in Sec ion 2.3) is e y inpu -
in ensi e and complex in i s calcula ion p ocedu e, many o he me hods ha e been de i ed
o de e mine he a e o e apo a ion. Depending on he inpu s o he me hod, we di ide
hem in o empe a u e-, adia ion-, mass ans e -based, and combined me hods.
Tempe a u e-based me hod equa ions can be conside ed he simples ype o equa ions.
They p ima ily wo k wi h a single a iable, namely he a e age mean ai empe a u e
Ta
.
Qui e o en hese equa ions ha e a linea o m
E=p Ta+q
, bu hey also occu in he
o m
E=k Tm
a
, o he o m o exponen ial o mula
E=
10
p Ta+q
o
E=
e
p Ta+q
. Howe e ,
he g oup also includes ela ions in which he empe a u e occu s in combina ion wi h a
membe comp ising, o ins ance, ela i e humidi y
RH
o heo e ical leng h o he sola day
N
.
In his sec ion, we selec ed 7 simple (in compa ison o he complexi y o FAO Penman–
Mon ei h) e apo a ion models o he demons a ion o ou calib a ion app oach.
2.4.1. Reg ession De i ed Rela ions—Czech Republic
The ollowing h ee ela ions a e used in he Czech Republic. They a e de i ed by
eg ession be ween he obse ed e apo a ion and mean daily ai empe a u e, using s a is-
ical eg ession o ind bo h linea and exponen ial models. The model ela ions p esen ed in
his sec ion a e compa ed in he pape [34] wi h measu emen s on 20m2e apo a ion pan
placed in he me eo ological s a ion Hlasi o nea he ci y o Tábo 49
◦
C290
0
N, 14
◦
C450
0
E)
in he Sou h Bohemian Region. This s a ion is ope a ed by Výzkumný ús a odohospodᡠský
T. G. Masa yka (VUV, T. G. Masa yk Wa e Resea ch Ins i u e) and was buil in 1957 and has
a
20m2
e apo a ion ank, GGI-3000 pan and Class-A pan. The pan e apo a ion measu e-
men s he e a e ca ied ou om May o Oc obe , which is due o he empe a u es below
he eezing poin in he win e mon hs. The models a e gi en by
ES=100.0452 Ta−0.204, (10)
EBV =0.2157 Ta+0.1133, (11)
EVUV =0.2157 Ta+0.726 u2−1.2259, (12)
whe e
ES
is he equa ion acco ding o Še me [
35
],
EBV
acco ding o Be an and Vizina [
36
],
and
EVUV
acco ding o Adam Be an om VUV published in he o icial epo Model
p ˚ubˇehu me eo ologických eliˇcin p o oblas jeze a Mos do oku 2050 (The modelling o he
cou se o me eo ological quan i ies o Lake Mos a ea un il 2050). In all equa ions, he
e apo a ion a e is de e mined in
[mmday−1]
. Equa ion
(10)
has he o m o an exponen ial
unc ion and he e o e i s esul s can ne e be nega i e. Howe e , i mus be men ioned
ha he e a e limi a ions o Equa ions
(11)
and
(12)
: i he equa ion p oduces he nega i e
e apo a ion es ima ion, we se he alue equal o ze o. Fo ins ance,
EBV =
0 is se on days
wi h he mean empe a u e below −0.526 °C, since EBV would be nega i e in such cases.
To calib a e he models, we p esen a pa ame ic o mula ion o he
Equa ions (10)–(12) by
ES(θ) = 10θ1Ta+θ2, (13)
EBV(θ) = max{θ1Ta+θ2,0}, (14)
EVUV(θ) = max{θ1Ta+θ2u2+θ3,0}, (15)
whe e
θ
a e unknown pa ame e s, which will be calib a ed. We ex ended models by
p ojec ion o nonnega i e numbe s (using he ou e
max
unc ion) o en o ce he compu ed
nonnega i e e apo a ion.
Wa e 2021,13, 1484 9 o 23
2.4.2. Kha u a
The equa ion p esen ed by Kha u a in [
37
] is an example o a nonlinea empe a u e
o mula. I is mos ly w i en in he li e a u e in he o m
EK=0.34 p T1.3
a(16)
and esul s in he e apo a ion a e in
[mmday−1]
. In
(16)
, a iable
p
deno es he pe cen age
o o al day ime hou s o he daily pe iod ou o o al day ime hou s o he yea . This
o m is used, o ins ance, in [
38
,
39
]. The coe icien 0.34 was ound empi ically and i is
possible o e ine i wi h espec o he si e-speci ic condi ions. Fo example, in [
34
], he
o m
EK=
0.25
p T1.3
a
is gi en wi h he o mula being calib a ed o he condi ions o he
Hlasi o wea he s a ion in he Sou h Bohemian Region. In his s udy, he o m
(16)
wi h
coe icien 0.34 is used.
In his pape , we he calib a e model (16) in oducing he pa ame ic e sion
EK(θ) = (θ1pTθ2
ai Ta>0,
0 i Ta≤0, (17)
and calib a e he unknown pa ame e s θ∈R2.
2.4.3. Ha g ea es–Samani
Ano he me hod was in oduced by Ha g ea es in a icle [
40
] and u he modi ied
o he o m which can be ound in a icle [
41
]. Usually, he Ha g ea es–Samani equa ion is
gi en in i s basic o m
EHS =0.0023 RaT1
2
(Ta+17.8).
In his equa ion, a iable
T
deno es he di e ence be ween daily maximum and
minimum ai empe a u es [°C].
Al hough he o mula con ains a adia ion e m
Ra
, i is anked among he empe a u e-
based o mulae since he e m
Ra
he e is jus a heo e ical alue calcula ed acco ding o
Fo mula
(5)
. Using his compu a ion o
Ra
, he Ha g ea es–Samani equa ion akes any o
he ollowing equi alen o ms
EHS =0.0023 Ra
λ(Ta+17.8)√T =0.0023(0.408 Ra)(Ta+17.8)√T =0.00094 Ra(Ta+17.8)√T .(18)
The di e ence o hese o ms is only in he usage o di ision by he la en hea o apo -
iza ion o wa e
λ=2.45MJkg−1
, which is pe o med o ob ain he esul s in millime es
pe day.
In his pape , we conside he pa ame ic o m o Ha g ea es–Samani Equa ion (18)
EHS(θ) = maxθ1Ra(Ta+θ2)√T
λ,0(19)
wi h pa ame e s
θ∈R2
. These pa ame e s will be op imized du ing he calib a ion p ocess.
2.4.4. Schendel
In con as o he o mulae men ioned abo e, in which he ai empe a u e is su icien
o calcula e he e apo a ion a e, he ai ela i e humidi y
RH
measu emen is equi ed in
he ollowing Schendel equa ion. The o mula has a simple o m
ESch =16 Ta
RH. (20)
The equa ion can be ound in he o iginal Schendel pape [
42
]. I is used by many
au ho s, o example, see [19,20].
Wa e 2021,13, 1484 16 o 23
Table 3.
The compa ison o s a is ical measu es be o e and a e he calib a ion p ocess o he
Kha u a equa ion. The i s ow ep esen s he alues o a ious s a is ical measu es (see columns)
o he o iginal model. Remaining ows de e mine he objec i e s a is ical measu e, which espec o
he model was calib a ed. The columns ep esen he co esponding alues o a ious measu es.
Ob ained Value
NSE RMSE MAE PBIAS
Calib a ion
objec i e
O iginal 0.6675858 1.0387729 0.7795765 15.480837
NSE 0.8511901 0.6950192 0.5481185 −1.191246
RMSE 0.8511973 0.6950022 0.5482104 −1.156551
MAE 0.8509640 0.6955467 0.5478520 −2.451671
PBIAS 0.8149230 0.7750987 0.6029666 0.003074
Table 4.
The compa ison o s a is ical measu es be o e and a e he calib a ion p ocess o he
Ha g ea es–Samani equa ion. The i s ow ep esen s he alues o a ious s a is ical measu es (see
columns) o he o iginal model. Remaining ows de e mine he objec i e s a is ical measu e, which
espec o he model was calib a ed. The columns ep esen he co esponding alues o a ious
measu es.
Ob ained Value
NSE RMSE MAE PBIAS
Calib a ion
objec i e
O iginal 0.8935767 0.5877587 0.4377886 10.9323242
NSE 0.9300600 0.4764787 0.3440658 −1.2411942
RMSE 0.9300550 0.4764958 0.3442857 −1.0261792
MAE 0.9298460 0.4772072 0.3432423 −2.2165424
PBIAS 0.9297419 0.4775611 0.3461323 0.0023911
Table 5.
The compa ison o s a is ical measu es be o e and a e he calib a ion p ocess o he Tu c
equa ion. The i s ow ep esen s he alues o a ious s a is ical measu es (see columns) o he
o iginal model. Remaining ows de e mine he objec i e s a is ical measu e, which espec o he
model was calib a ed. The columns ep esen he co esponding alues o a ious measu es.
Ob ained Value
NSE RMSE MAE PBIAS
Calib a ion
objec i e
O iginal 0.6675858 1.03877290 0.7795765 15.4808373
NSE 0.8511901 0.6950192 0.5481185 −1.1912456
RMSE 0.8511973 0.6950022 0.5482104 −1.1565508
MAE 0.8509640 0.6955467 0.5478520 −2.4516705
PBIAS 0.8149230 0.7750987 0.6029666 0.0030740
As we men ioned abo e, he andom choice o calib a ion da a in he calib a ion
p ocess causes he andomness o he op imal pa ame e s. In Figu es 5–7, we p esen he
di e en op imal alues o calib a ed models wi h espec o a ious s a is ical measu es.
We can obse e ha using he c oss- alida ion app oach, he inal op imal pa ame e s a e
a andom a iable as well.
The calib a ion p ocess i s he model o he alues compu ed by he FAO Penman–
Mon ei h equa ion. We demons a e his capabili y on speci ic examples. Figu es 8–10
p esen he compa ison o mon hly e apo a ion compu ed by FAO Penman–Mon ei h
Equa ion (1)
, Ha g ea es–Samani Equa ion
(16)
, and calib a ed Ha g ea es–Samani Equa-
ion
(17)
in he o m o cumula i e sum and he sca e plo . The calib a ion has been
pe o med wi h espec o NSE.

Wa e 2021,13, 1484 17 o 23
Figu e 5.
The compa ison o he calib a ed Kha u a model pa ame e s ob ained by he c oss- alida ion calib a ion p ocess
on aining da a wi h espec o a ious s a is ical measu es.
Figu e 6.
The compa ison o he calib a ed Ha g ea es–Samani model pa ame e s ob ained by he c oss- alida ion
calib a ion p ocess on aining da a wi h espec o a ious s a is ical measu es.
Figu e 7. The compa ison o he calib a ed Tu c model pa ame e s ob ained by he c oss- alida ion calib a ion p ocess on
aining da a wi h espec o a ious s a is ical measu es.
Wa e 2021,13, 1484 18 o 23
Figu e 8.
The compa ison o he daily e apo a ion compu ed by FAO Penman–Mon ei h equa ion, Kha u a equa ion, and
calib a ed Kha u a equa ion wi h espec o NSE in he o m o cumula i e e apo a ion (le ) and he sca e plo ( igh ).
Figu e 9.
The compa ison o he daily e apo a ion compu ed by FAO Penman–Mon ei h equa ion, Ha g ea es–Samani
equa ion, and calib a ed Ha g ea es–Samani equa ion wi h espec o NSE in he o m o cumula i e e apo a ion (
le
) and
he sca e plo ( igh ).
Figu e 10.
The compa ison o he daily e apo a ion compu ed by FAO Penman–Mon ei h equa ion, Tu c equa ion, and
calib a ed Tu c equa ion wi h espec o NSE in he o m o cumula i e e apo a ion (le ) and he sca e plo ( igh ).
Wa e 2021,13, 1484 19 o 23
The inal esul is p esen ed in Figu e 11. He e, we demons a e he mon hly e apo a-
ion compu ed by Ha g ea es–Samani equa ion in he o m o a ime-line and his og am o
e apo a ion in mon hs. The pa ame e s o he calib a ed models can be ound in Table 2
and he imp o emen o he used s a is ical measu e on he whole da a se in Table 1.
Figu e 11.
The compa ison o he mon hly e apo a ion compu ed by FAO Penman–Mon ei h equa ion, Ha g ea es–Samani
equa ion, and calib a ed Ha g ea es–Samani equa ion. The calib a ion has been pe o med using a ious s ochas ic
measu es.
Wa e 2021,13, 1484 20 o 23
4. Discussion
In ou esul s p esen ed in he p e ious sec ion, we p ocessed he esul s o calib a ion
on andom da a om he c oss- alida ion p ocess (see Sec ion 2.6). Be o e he selec ion o
he mean model, we emo ed he ou lie s based on he qua ile h esholding. Fo ins ance,
in he case o he Kha u a equa ion calib a ed wi h espec o
NSE
, we emo ed 11 ou lie s
mo e han 1.5 in e qua ile anges (IQRs) below he i s qua ile o abo e he hi d qua ile.
Ou esul s show ha he calib a ed pa ame e s depend on he chosen s a is ical
measu e, see Table 2. Howe e , all o hem a e imp o ing he objec i e alue in compa ison
wi h he o iginal equa ions, see Table 1.
F om he ob ained esul s, we obse ed ha he calib a ion wi h espec o one se-
lec ed measu e imp o es no only his objec i e measu e bu also imp o es he emaining
measu es. See Tables 3–5, whe e we examined he Kha u a, Ha g ea es–Samani, and
Tu c model.
The measu es p esen ed in Sec ion 2.5 a e de ined as he sum o local di e ences. Ou
esul s o cumula i e e apo a ion p esen ed in Figu es 8–10 show he consequences o he
o mula ion o he objec i e unc ion in his o m— he cumula i e e apo a ion compu ed
by he op imal calib a ed model i s he cumula i e e apo a ion compu ed by he
FAO
equa ion. We obse ed his p ope y in he case o all measu es. Howe e , in he case o
daily e apo a ion (o mon hly e apo a ion), he local di e ence can be la ge, see
Figu e 11
.
E apo a ion in some mon hs has been unde es ima ed and in o he mon hs has been
o e es ima ed. In any case, his unde es ima ion and o e es ima ion a e always be e han
in he case o he o iginal equa ion.
The ob ained esul s ollow he equi alency o he calib a ion p ocess based on
NSE
maximiza ion and
RMSE
minimiza ion, i.e., Theo em 1. Please see Figu es 5–7, whe e we
demons a e he densi y o op imal pa ame e s o he calib a ed Kha u a, Ha g ea es–
Samani, and Tu c equa ion wi h espec o he andom da a spli in he c oss- alida ion
p ocess. The small di e ence be ween
NSE
and
RMSE
is caused by he e o o he i e a i e
algo i hm: he op imiza ion algo i hm has a s opping c i e ium based on he change o he
unc ion alue. Since he
NSE
and
RMSE
ha e di e en objec i e unc ions, he i e a i e
algo i hm s ops he op imiza ion p ema u ely (su icien ly app oxima ely) in di e en
op imize s. Especially in he case o Figu e 6, he di e ence is clea ly obse able. Howe e ,
in his case, we a e dealing wi h he Ha g ea es–Samani model
(19)
. We suppose ha
his di e ence is caused by he non-linea i y o he model (and he non-linea i y o used
s a is ical measu es). The di e ence be ween objec i e unc ions in he solu ions compu ed
by
NSE
and
RMSE
is app oxima ely 10
−2
(see Table 4), which is he alue used in he
s opping c i e ia o he i e a i e op imiza ion algo i hm. The si ua ion is simila o
RMSE
.
The esul s ob ained by ou analysis show ha he calib a ed Ha g ea es–Samani and
Tu c models seem o be he mos sui able simpli ica ion o he FAO Penman–Mon ei h
equa ion in he a ea o Lake Mos . Howe e , i is necessa y o men ion ha he inal choice
o he mos sui able calib a ed equa ion o e apo a ion modelling depends no only on he
inal alue o he s a is ical measu es bu also on he inpu da a equi emen s. The e o e,
we sugges using he Ha g ea es–Samani equa ion since his equa ion equi es only he
inpu o he ex a e es ial adia ion and he ai empe a u e, see Equa ion
(18)
. Figu e 11
p esen s he inal imp o ed e apo a ion es ima ion.
5. Conclusions
In his pape , we p esen ed he me hodology o he calib a ion o e apo a ion models
wi h he FAO Penman–Mon ei h equa ion and demons a ed i on selec ed simpli ied
models using he mos common s a is ical measu es. Addi ionally, we implemen ed a c oss-
alida ion p ocess o emo e he o e i ing o he calib a ed model. This app oach can be
easily applied o any model o in e es and any su icien ly easonable s a is ical measu e.
In he pape , we p esen ed a calib a ion wi h espec o heo e ical alues compu ed by
FAO Penman–Mon ei h equa ion; howe e , he me hodology can be used o calib a ion
wi h any heo e ical o measu ed e e ence alues o e apo a ion.
Wa e 2021,13, 1484 21 o 23
F om he p esen ed esul s, we sugges using he Ha g ea es–Samani equa ion o
model he e apo a ion on Lake Mos . This equa ion epo ed he su icien app oxima ion
o he FAO Penman–Mon ei h equa ion and addi ionally, i equi es only a ew inpu
pa ame e s, which can be easily (and cheaply) measu ed.
Du ing ou esea ch, we obse ed he global i ing p ope y o common s a is ical
measu es— he e apo a ion du ing cold days is unde es ima ed and he e apo a ion du ing
sunny days is o e es ima ed. To deal wi h his issue, we ocus ou u u e wo k on he
di ision o days in o g oups wi h di e en op imal models.
Au ho Con ibu ions:
Concep ualiza ion, V.D. and D.D.; me hodology, V.D., L.P.; so wa e, V.D.;
alida ion, V.D.; o mal analysis, L.P. and V.D.; in es iga ion, V.D. and D.D.; esou ces, D.D. and V.D.;
da a cu a ion, V.D. and D.D.; w i ing—o iginal d a p epa a ion, V.D. and D.D.; w i ing— e iew and
edi ing, L.P.; isualiza ion, V.D.; supe ision, D.D.; p ojec adminis a ion, D.D.; unding acquisi ion,
D.D. All au ho s ha e ead and ag eed o he published e sion o he manusc ip .
Funding:
This pape has been comple ed hanks o he inancial suppo p o ided o VSB-Technical
Uni e si y o Os a a by he Czech Minis y o Educa ion, You h and Spo s om he budge o
concep ual de elopmen o science, esea ch and inno a ions o he 2021 yea and he Depa men
o Ma hema ics a he Facul y o Ci il Enginee ing, VSB-Technical Uni e si y o Os a a.
Ins i u ional Re iew Boa d S a emen : No applicable.
In o med Consen S a emen : No applicable.
Da a A ailabili y S a emen :
The da a a e no publicly a ailable due o he equi emen s o con i-
den iali y and secu i y. Da a was ob ained om The Ins i u e o A mosphe ic Physics CAS and a e
a ailable om he au ho s wi h he pe mission o The Ins i u e o A mosphe ic Physics CAS.
Acknowledgmen s:
The au ho s would like o exp ess u he hanks o The Ins i u e o A mosphe ic
Physics CAS o he p o ided me eo ological da a om hei measu ing s a ion Kopis y.
Con lic s o In e es : The au ho s decla e no con lic o in e es .
Abb e ia ions
The ollowing abb e ia ions a e used in his manusc ip :
EFAO FAO Penman–Mon ei h Equa ion (1),
ESŠe me Equa ion (10),
EBV Be an-Vizina Equa ion (11),
EVUV he equa ion ecommended by T. G. Masa yk Wa e Resea ch Ins i u e (12),
EKKha u a Equa ion (16),
EHS Ha g ea es–Samani Equa ion (18),
ESch Schendel Equa ion (20),
EPT P ies ley–Taylo Equa ion (22),
PBIAS Pe cen age Bias (29),
MAE Mean Absolu e E o (28),
RMSE Roo Mean Squa e E o (27),
NSE Nash–Su cli e E iciency (26),
Ta he a e age ai empe a u e [°C],
Tmax,Tmin maximal and minimal ai empe a u e [°C],
T he di e ence be ween daily maximum and minimum ai empe a u es [°C],
Pa mosphe ic p essu e [kPa],
ppe cen age o o al day ime hou s o he pe iod used (daily o mon hly) ou o o al
day ime hou s o he yea .
RH ela i e humidi y [%],
Ra he ex a e es ial adia ion hMJm−2day−1i,
Rnne adia ion [kJ ·m−2·s−1],
Rs he sola adia ion hMJ m−2day−1i,

Wa e 2021,13, 1484 22 o 23
Rso he clea -sky adia ion hMJ m−2day−1i,
γ he psych ome ic cons an [m·s−1],
σS e an-Bol zmann cons an σ=4.903 ×10−9MJK−4m−2day−1
λla en hea o apo iza ion λ=2.45 MJ kg−1,
Cp he speci ic hea o ai , Cp=1013 Jkg−1°C−1,
ρa he ai densi y kg m−3,
∆ he slope o sa u a ion apo p essu e cu e [kPa ·[°C]−1],
u2wind speed a heigh 2m m s−1,
G he hea low in he soil [MJ m−2day−1],
esmean sa u a ion apo p essu e [kPa],
ea he cu en wa e apo p essu e [kPa],
es−ea apo p essu e de ici [kPa].
Re e ences
1.
Allen, R.G.; Pe ei a, L.; Raes, D.; Smi h, M. C op E apo anspi a ion-Guidelines o Compu ing C op Wa e Requi emen s-FAO I iga ion
and D ainage Pape 56; Uni ed Na ion-Food and Ag icul u e o ganisa ion: Rome, I aly, 1998; Volume 56.
2.
Jensen, M.E.; Allen, R.G. E apo a ion, E apo anspi a ion, and I iga ion Wa e Requi emen s, 2nd ed.; Ame ican Socie y o Ci il
Enginee s: Res on, VA, USA, 2016. [C ossRe ]
3.
Gallego-El i a, B.; Baille, A.; Ma in-Go iz, B.; Maes e, J.; Ál a ez, V. E alua ion o e apo a ion es ima ion me hods o a
co e ed ese oi in a semi-a id clima e (sou h-eas e n Spain). J. Hyd ol. 2012,458, 59–67. [C ossRe ]
4.
C aig, I. Compa ison o p ecise wa e dep h measu emen s on ag icul u al s o ages wi h open wa e e apo a ion es ima es.
Ag ic. Wa e Manag. 2006,85, 193–200. [C ossRe ]
5.
Sca o, F.B.; Ma co Tina, G.; Gagliano, A. Compa ison o e apo a ion models o ee wa e basins su aces. In P oceedings o he
2019 4 h In e na ional Con e ence on Sma and Sus ainable Technologies (SpliTech), Spli , C oa ia, 18–21 June 2019; pp. 1–7.
[C ossRe ]
6.
Abd-Elhamid, H.F.; Ahmed, A.; Zeleˇnáko á, M.; V anayo á, Z.; Fa hy, I. Rese oi Managemen by Reducing E apo a ion Using
Floa ing Pho o ol aic Sys em: A Case S udy o Lake Nasse , Egyp . Wa e 2021,13, 769. [C ossRe ]
7.
Kohli, A.; F enken, K. E apo a ion om A i icial Lakes and Rese oi s; AQUASTAT P og amme, Uni ed Na ion-Food and
Ag icul u e O ganisa ion: Rome, I aly, 2015.
8.
Jabloun, M.; Sahli, A. E alua ion o FAO-56 me hodology o es ima ing e e ence e apo anspi a ion using limi ed clima ic da a:
Applica ion o Tunisia. Ag ic. Wa e Manag. 2008,95, 707–715. [C ossRe ]
9.
Ga ilán, P.; Be engena, J.; Allen, R.G. Measu ing e sus es ima ing ne adia ion and soil hea lux: Impac on Penman–Mon ei h
e e ence ET es ima es in semia id egions. Ag ic. Wa e Manag. 2007,89, 275–286. [C ossRe ]
10.
Lo elli, S.; Pizza, S.; Caponio, T.; Ri elli, A.; Pe niola, M. Lysime ic de e mina ion o muskmelon c op coe icien s cul i a ed
unde plas ic mulches. Ag ic. Wa e Manag. 2005,72, 147–159. [C ossRe ]
11.
Tolasz, R. A las podnebí ˇ
Ceska (Clima e a las o Czechia); Uni e zi a Palackého Olomouci- ˇ
CHMU: Olomouc, Czech Republic, 2007.
12.
Dlouhá, D.; Dubo ský, V. The Imp o emen o he Lake Mos E apo a ion Es ima es. In˙
zynie ia Mine alna
2019
,43, 159–164.
[C ossRe ]
13. B u sae , W. Hyd ology: An In oduc ion; Camb idge Uni e si y P ess: Camb idge, UK, 2005. [C ossRe ]
14.
McMahon, T.; Finlayson, B.; Peel, M. His o ical de elopmen s o models o es ima ing e apo a ion using s anda d me eo ological
da a. Wiley In e discip. Re . Wa e 2016,3, 788–818. [C ossRe ]
15. B u sae , W. E apo a ion in o he A mosphe e: Theo y, His o y, and Applica ions; Sp inge : Do d ech , The Ne he lands, 1982.
16. Maidmen , D. Handbook o Hyd ology; McG aw-Hill Educa ion: New Yo k, NY, USA, 1993.
17.
Ab ew, W.; Melesse, A. E apo a ion and E apo anspi a ion: Measu emen s and Es ima ions; Sp inge : Be lin/Heidelbe g, Ge many,
2012. [C ossRe ]
18. Bedien , P.; Hube , W.; Vieux, B. Hyd ology and Floodplain Analysis; Pea son: New Yo k, NY, USA, 2013.
19.
Bo mann, H. Sensi i i y analysis o 18 di e en po en ial e apo anspi a ion models o obse ed clima ic change a Ge man
clima e s a ions. Clim. Chang. 2010,104, 729–753. [C ossRe ]
20.
Taba i, H.; G isme , M.; T ajko ic, S. Compa a i e Analysis o 31 Re e ence E apo anspi a ion Me hods unde Humid Condi ions.
I ig. Sci. 2011,31, 107–117. [C ossRe ]
21.
Lang, D.; Zheng, J.; Shi, J.; Liao, F.; Ma, X.; Wang, W.; Chen, X.; Zhang, M. A Compa a i e S udy o Po en ial E apo anspi a ion
Es ima ion by Eigh Me hods wi h FAO Penman–Mon ei h Me hod in Sou hwes e n China. Wa e 2017,9, 734. [C ossRe ]
22.
Mohawesh, O. E alua ion o e apo anspi a ion models o es ima ing daily e e ence e apo anspi a ion in a id and semia id
en i onmen s. Plan Soil En i on. 2011,57, 145–152. [C ossRe ]
23.
Mos a a, A.; Benzagh a, M.; Benzagh a, A.; Mohammed, A.; Ekhmaj, A. P edic ion o E apo a ion om Alga dabiya Rese oi .
Libyan Ag ic. Res. Cen . J. In . 2012,3, 120–128. [C ossRe ]
Wa e 2021,13, 1484 23 o 23
24.
Djaman, K.; Balde, A.; Sow, A.; Mulle , B.; I mak, S.; N’Diaye, M.; Manneh, B.; Moukoumbi, Y.D.; Fu akuchi, K.; Sai o, K.
E alua ion o six een e e ence e apo anspi a ion me hods unde sahelian condi ions in he Senegal Ri e Valley. J. Hyd ol. Reg.
S ud. 2015,3, 139–159. [C ossRe ]
25.
Yao, H. Long-Te m S udy o Lake E apo a ion and E alua ion o Se en Es ima ion Me hods: Resul s om Dickie Lake,
Sou h-Cen al On a io, Canada. J. Wa e Resou . P o . 2009,2, 59–77. [C ossRe ]
26.
Cab e a, M.C.M.; Anache, J.A.A.; Youl on, C.; Wendland, E. Pe o mance o e apo a ion es ima ion me hods compa ed wi h
s anda d 20 m2 ank. Re . B as. Eng. Ag Ãcola Ambien . 2016,20, 874–879. [C ossRe ]
27.
Mo iasi, D.; A nold, J.; Van Liew, M.; Bingne , R.; Ha mel, R.; Vei h, T. Model E alua ion Guidelines o Sys ema ic Quan i ica ion
o Accu acy in Wa e shed Simula ions. T ans. ASABE 2007,50, 885–900. [C ossRe ]
28.
S one, M. C oss- alida o y choice and assessmen o s a is ical p edic ions. J. R. S a . Soc. Se . Me hodol.
1974
,36, 111–147.
[C ossRe ]
29.
Dubo ský, V.; Dlouhá, D.; Pospíšil, L. The Calib a ion o E apo a ion Models agains he Penman–Mon ei h Equa ion on Lake
Mos . Sus ainabili y 2020,13, 313. [C ossRe ]
30. Pali o ý Kombiná Ús í (PKU) O icial Web Page. A ailable online: h ps://www.pku.cz/ (accessed on 13 Ap il 2021).
31.
Linac e, E. Da a-spa se es ima ion o lake e apo a ion, using a simpli ied Penman equa ion. Ag ic. Fo . Me eo ol.
1993
,64, 237–256.
[C ossRe ]
32.
Debna h, S.; Adamala, S.; Raghuwanshi, N. Sensi i i y Analysis o FAO-56 Penman-Mon ei h Me hod o Di e en Ag o-
ecological Regions o India. En i on. P ocess. 2015,2, 689–704. [C ossRe ]
33.
Taba i, H.; Hosseinzadeh Talaee, P. Sensi i i y o e apo anspi a ion o clima ic change in di e en clima es. Glob. Plane . Chang.
2014,115, 16–23. [C ossRe ]
34.
Anso ge, L.; Be an, A. Pe o mance o simple empe a u e-based e apo a ion me hods compa ed wi h a ime se ies o pan
e apo a ion measu es om a s anda d 20 m2 ank. J. Wa e Land De . 2019,41, 1–11. [C ossRe ]
35.
Še me , A. Expe imen álné zo ce p e s ano enie s á ody ýpa om z odných nád ží [Empi ical equa ions o es ima ion o
e apo a ion om ese oi s]. Vodní Hospodᡠs í 1961,12, 544–547.
36.
Be an, A.; Vizina, A. Od ození eg esních z ah˚u p o ýpoˇce ýpa u z olné hladiny a iden i ikace end˚u e ý oji mˇeˇ ených
eliˇcin e ýpa omˇe né s anici Hlasi o [De i a ion o eg ession equa ions o calcula ion o e apo a ion om a ee wa e
su ace and iden i ica ion o ends in measu ed a iables in Hlasi o s a ion]. Vodohospodᡠské Technicko-Ekonomické In .
2013
,
55, 4–8.
37. Kha u a, N. Simpli ied equa ion o e apo anspi a ion in a id egions. Hyd ol. Sonde h. 1985,5, 39–47.
38.
Xu, C.; Singh, V.P. E alua ion and gene aliza ion o empe a u e-based me hods o calcula ing e apo a ion. Hyd ol. P ocess.
2001,15, 305–319. [C ossRe ]
39.
Poyen, C.E.F.; Ghosh, D.; Palash Kundu, D. Tempe a u e based ET Me hod Selec ion o Bu dwan Dis ic in WB, INDIA. In . J.
Appl. Eng. Res. 2018,13, 12753–12763.
40. Ha g ea es, G. Mois u e A ailabili y and C op P oduc ion. T ans. ASABE 1975,18, 980–984. [C ossRe ]
41. Ha g ea es, G.; Samani, Z. Re e ence C op E apo anspi a ion F om Tempe a u e. Appl. Eng. Ag ic. 1985,1, 96–99. [C ossRe ]
42. Schendel, U. Vege a ionswasse e b auch und-wasse beda . Habili . Kiel 1967,137, 1–11.
43.
P ies ley, C.H.B.; Taylo , R.J. On he Assessmen o Su ace Hea Flux and E apo a ion Using La ge-Scale Pa ame e s. Mon.
Wea he . Re . 1972,100, 81–92. [C ossRe ]
44.
Tu c, L. Es ima ion o i iga ion wa e equi emen s, po en ial e apo anspi a ion: A simple clima ic o mula e ol ed up o da e.
Ann. Ag on. 1961,12, 13–49.
45.
Xu, C.; Singh, V.P. E alua ion and Gene aliza ion o Radia ion-based Me hods o Calcula ing E apo a ion. Hyd ol. P ocess.
2000
,
14, 339–349. [C ossRe ]
46.
Nash, J.; Su cli e, J. Ri e low o ecas ing h ough concep ual models pa I—A discussion o p inciples. J. Hyd ol.
1970
,
10, 282–290. [C ossRe ]
47. R Co e Team. R: A Language and En i onmen o S a is ical Compu ing; R Founda ion o S a is ical Compu ing: Vienna, Aus ia,
2013.
48. Gay, D.M. Usage summa y o selec ed op imiza ion ou ines. Compu . Sci. Tech. Rep. 1990,153, 1–21.