scieee Science in your language
[en] (orig)

Predicting the Optimum Corn Harvest Time via the Quantity of Dry Matter Determined with Vegetation Indices Obtained from Multispectral Field Imaging

Abstract

Estimating the optimum harvest time and yield embodies an essential food security factor. Vegetation indices have proven to be an effective tool for widescale in-field plant health mapping. A drone-based multispectral camera then conveniently allows acquiring data on the condition of the plant. This article examines and discusses the relationships between vegetation indices and nutritiolnal values that have been determined via chemical analysis of plant samples collected in the field. In this context, emphasis is placed on the normalized difference red edge index (NDRE), normalized difference vegetation index (NDVI), green normalized difference vegetation index (GNDVI), and nutritional values, such as those of dry matter. The relationships between the variables were correlated and described by means of regression models. This produced equations that are applicable for estimating the quantity of dry matter and thus determining the optimum corn harvest time. The obtained equations were validated on five different types of corn hybrids in fields within the South Moravian Region, Moravia, the Czech Republic.

Read accessible full text

Predicting the Optimum Corn Harvest Time via the Quantity of Dry Matter Determined with Vegetation Indices Obtained from Multispectral Field Imaging

Author: Janoušek, Jiří; Marcoň, Petr; Dohnal, Přemysl; Jambor, Václav; Synková, Hana; Raichl, Petr
Publisher: MDPI
Year: 2023
DOI: 10.3390/rs15123152
Source: https://dspace.vut.cz/bitstreams/98d07778-a7fb-4ad1-b3c4-f8dbbb62e93a/download
Ci a ion: Janoušek, J.; Ma coˇn, P.;
Dohnal, P.; Jambo , V.; Synko á, H.;
Raichl, P. P edic ing he Op imum
Co n Ha es Time ia he Quan i y
o D y Ma e De e mined wi h
Vege a ion Indices Ob ained om
Mul ispec al Field Imaging. Remo e
Sens. 2023,15, 3152. h ps://doi.o g/
10.3390/ s15123152
Academic Edi o : Guido D’U so
Recei ed: 24 Ap il 2023
Re ised: 7 June 2023
Accep ed: 14 June 2023
Published: 16 June 2023
Copy igh : © 2023 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/).
emo e sensing
A icle
P edic ing he Op imum Co n Ha es Time ia he Quan i y o
D y Ma e De e mined wi h Vege a ion Indices Ob ained om
Mul ispec al Field Imaging
Jiˇ íJanoušek 1, Pe Ma coˇn 1,* , Pˇ emysl Dohnal 1, Václa Jambo 2, Hana Synko á2and Pe Raichl 1
1Facul y o Elec ical Enginee ing and Communica ion, B no Uni e si y o Technology,
61600 B no, Czech Republic; xjanou09@ u b .cz (J.J.); [email p o ec ed] (P.D.); [email p o ec ed] (P.R.)
2Nu iVe s. .o., Vídeˇnská1023, 69123 Pohoˇ elice, Czech Republic; jambo [email p o ec ed] (V.J.);
[email p o ec ed] (H.S.)
*Co espondence: ma [email p o ec ed]
Abs ac :
Es ima ing he op imum ha es ime and yield embodies an essen ial ood secu i y
ac o . Vege a ion indices ha e p o en o be an e ec i e ool o widescale in- ield plan heal h
mapping. A d one-based mul ispec al came a hen con enien ly allows acqui ing da a on he
condi ion o he plan . This a icle examines and discusses he ela ionships be ween ege a ion
indices and nu i iolnal alues ha ha e been de e mined ia chemical analysis o plan samples
collec ed in he ield. In his con ex , emphasis is placed on he no malized di e ence ed edge index
(NDRE), no malized di e ence ege a ion index (NDVI), g een no malized di e ence ege a ion
index (GNDVI), and nu i ional alues, such as hose o d y ma e . The ela ionships be ween he
a iables we e co ela ed and desc ibed by means o eg ession models. This p oduced equa ions
ha a e applicable o es ima ing he quan i y o d y ma e and hus de e mining he op imum co n
ha es ime. The ob ained equa ions we e alida ed on i e di e en ypes o co n hyb ids in ields
wi hin he Sou h Mo a ian Region, Mo a ia, he Czech Republic.
Keywo ds:
co n; mul ispec al imaging; ege a ion indices; nu i ional analysis; co ela ion; pho-
og amme y; op imal ha es ime; UAV
1. In oduc ion
1.1. Remo e Sensing
The emo e sensing o he Ea h’s su ace has assumed a signi ican ole in p ecision
ag icul u e, and has main ained his posi ion on a long- e m basis. Imaging ag icul u al
a eas is enabled h ough sa elli es and hype spec al o mul ispec al came as [
1
]. These
a e employed no only in emo e sensing, bu also, o example, in de ec ing dying ees in-
es ed wi h pes s [
2
], o en o mechanically damaged ui and ege ables [
3
], ecognizing
ecal pollu ion [
4
], es ablishing cold-induced de e io a ion o cucumbe s [
5
], measu ing
ui ipening [
6
], classi ying whea ke nels in ec ed wi h ungi [
7
], and many o he ap-
plica ions [
8
,
9
]. Recen ly, he ac ual app oach and associa ed me hodologies ha e been
de eloping subs an ially.
The esea ch ou lined he ein exploi s a p e iously published case s udy [
1
], hus
building on, e i ying, and ma kedly enhancing an al eady es ablished co ela ion be ween
plan nu i ional alues and ege a ion indices. Impo an ly, ou la es conclusions we e
o mula ed om da a measu ed o e h ee yea s, i.e., h ee ha es seasons, while he
e e enced a icle [1] p esen s and analyzes esul s ob ained du ing one season only.
The o al ha es ed c op biomass consis s o whole co n plan s. The basic indica o o
plan phenophase is based on speci ying he d y ma e con en s; hese inc ease signi ican ly
as he c op ma u es. In co n, he d y ma e cha ac e izes he g ow h ma u i y le el, and
i s olume in luences he silage quali y ma e ially and p ocedu ally [
10
]. The chemical
Remo e Sens. 2023,15, 3152. h ps://doi.o g/10.3390/ s15123152 h ps://www.mdpi.com/jou nal/ emo esensing
Remo e Sens. 2023,15, 3152 2 o 19
composi ion o co n plan s changes o e he cou se o he g owing pe iod. Be o e he
plan de elops ea s, i s ene gy is concen a ed mainly in he ibe , whose p opo ion a ies
be ween plan s, depending on he ac ual ha es ime. To ensu e ha he inal co n silage
p oduc comp ises no only ibe bu also s a ch, he ha es ing has o be pe o med a he
wax ma u i y s age, namely, when he d y ma e p opo ion alues in he whole plan
each be ween 280 and 330 g/kg. In such cases, he milk line s age a ains 2/3 o he co n
g ain. Ano he indica o o g ow h ma u i y is he abili y o be ensiled, o , in o he wo ds,
o gene a e e men a ion acids ha p ese e he silage.
The ha es ing ime and he o al amoun o biomass ha e an essen ial impac on he
cha ac e o he silage e men a ion. The quali y o he co n cul i a ion p ocesses and he
subsequen ensiling ollows om he wea he condi ions in a pa icula yea , he choice o
a sui able hyb id wi h an app op ia e FAO numbe o speci y he ea liness le el, ea men ,
and cha ac e o sowing.
Co n samples a e ou inely collec ed a di e se loca ions in he ield o allow he
assessing o he condi ion and phenophase. When he milk line s age has been eached, he
samples a e submi ed o a labo a o y o chemical analysis o de e mine he d y ma e
con en in bo h he g ain and he whole plan . Depending on he deg ee o which he
plan and he d y ma e ha e de eloped, he ha es ing ime is se p elimina ily, a ying
acco ding o he planned a ge use o he co n, namely, milk p oduc ion o me hane
gene a ion a biogas acili ies.
As he d y ma e con en embodies a majo pa ame e o de ining he op imum
ha es ime, i is impo an o es ablish whe he mo e accu a e da a can be ob ained on he
a e age d y ma e alue wi hin an en i e, non-homogeneous ield. This a icle p oposes
o sol e he p oblem using an e ec i e in eg a ion o di e en me hods and echnologies,
in ol ing a d one wi h a mul ispec al came a, image da a analysis o acqui e ege a ion
indices, and a chemical analysis o all samples collec ed in he ield.
1.2. Field-Wide Image Da a Cap u ing
Comp ehensi e da a ela ing o he condi ion o a ield and hus also he a e age
con en o d y ma e a e ob ainable ia one o wo undamen al echnologies, namely,
sa elli e image y o pho og amme y pe o med by using a mul ispec al o hype spec al
came a moun ed on an ae ial ehicle. Bo h o hese app oaches can be applied o p edic
he yield o ag icul u al c ops.
Pho og amme ic imaging wi h unmanned ae ial ehicles (UAVs) u ilizes di e en
ypes o mul ispec al o hype spec al came as [
11
–
16
]. The p oblem o c op yield p edic-
ion om pho og amme ic da a acqui ed by UAVs has been add essed in he li e a u e [
11
].
Ou a icle expands on he p e ious esea ch, p esen ing no el indings ega ding he co -
ela ion be ween d y ma e yield and ege a ion indices.
The o he o he wo imaging op ions elies on sa elli es. Sa elli e image y di e s om
he UAV-based me hod in he dis ance o he senso om he a ea o in e es . Sa elli es mo e
a a cons an al i ude o no less han 400 km along o bi s—ei he geos a iona y ones, which
ci cle he Ea h abo e he equa o , o o he s. Impo an ly, he sa elli es wi h he la e ype
e ol e a ound he Ea h p og essi ely o e i s en i e su ace, in a no h–sou h di ec ion.
A i icial sa elli es ensu e egula imaging wi h long s abili y and epea abili y o e
ime, and hese aspec s embody he mos signi ican ad an age o he echnique. By
con as , he main d awback es s in a lowe image esolu ion, an issue ha subs an ia es
he use o d ones in compiling high esolu ion maps. The sa elli es allow us o easily
de e mine hei ime o passage o e he a ea being moni o ed; such ime, howe e , canno
be adjus ed acco ding o need o o sui he posi ion o he a ea o in e es , as he o bi ing
speed emains cons an . Fu he mo e, ob aining high quali y images depends on a o able
wea he incompa ably mo e han in UAV econnaissance; he p ocess is ulne able o
cons aining e ec s ha include, o ins ance, cloud bands.
Remo e Sens. 2023,15, 3152 3 o 19
Sa elli es ca y key senso s, such as mul ispec al and hype spec al senso s, lida s,
and RGB came as. Access o he images is ne e heless o en limi ed, equi ing p e-paid
se ices ha p o ide an image da abase.
The la ges numbe o sa elli es a e ope a ed by he US-based company Plane Labs
wi hin he Plane Scope, a sys em comp ising 175 sa elli es ha supply mul ispec al images
wi h a spa ial esolu ion o up o 3 m; he imaging is pe o med daily and co e s he en i e
su ace o he Ea h. The p ocessing u ilizes aw da a, applying a mosphe ic co ec ions
and o he ele an p ocedu es, such as single-pixel classi ica ion [17,18].
1.3. P edic ing C op Yield
The p edic ion o c op yield ia sa elli e image y has been discussed in mul iple
esea ch a icles. In his con ex , o ins ance, he au ho s o s udy [
19
] ocus on he op imum
ime o apply ni ogen chemicals o c ops a a e y ea ly g ow h s age, in es iga ing he
ac ual iming oge he wi h measu emen o he ege a ion index NDVI and plan heigh
as an indica o o d y ma e ou pu ; howe e , despi e his comp ehensi e app oach, only
ela i e alues o e wo yea s a e p o ided.
A icle [
20
] examines eg ession models o c op yield es ima ion ia he NDVI index
and measu emen o he ela i e c op ou pu (paddy ice, win e whea , and co n). The
au ho s iden i y he bes pe iod o es ima ing he c op yield eliably, cha ac e izing he
model ha showed a oo mean squa e e o o 206.59 kg/ha in co n as he bes i . The
models pe o m easonably well in small egions, especially in a eas whe e he c op ypes
a e no exac ly known.
In s udy [
21
], he NDVI was ound o deli e an excellen a e o co ela ion wi h yield
alues, albei wi h a delay o 4–6 weeks, in g ass used o biomass. In co n, he yield alue
co ela es wi h he NDVI wi h a delay o wo weeks.
Measu emen s ha ely on spec o adiome ic equipmen , whe e he ac i e adia ion
sou ce o an NDVI measu emen is ac i e, show s ong co ela ions be ween he NDVI and
du um whea geno ypes. A ela ed a icle [
22
] ne e heless also sugges s ha he measu ing
p ocedu es may ma kedly depend on he spec ome e used, mainly as ega ds hei o e all
sui abili y o he pu pose and he ope a ing ime equi ed. Th ough he ou comes o o he
esea ch p ojec s [
23
–
25
], he Mode a e Resol ed Imaging Spec o adiome e (MODIS)
appea s o p oduce good esul s when p edic ing ha es olumes. Co n yield p edic ion
and unce ain y analysis based on emo ely sensed a iables using a Bayesian neu al
ne wo k is add essed in s udy [
26
]. O he a i icial in elligence me hods o es ima ing c op
yield quan i a i ely a e p esen ed wi hin sou ces [27–33].
In e es ingly, a signi ican co ela ion has been e ealed be ween s ess-exposed co n
plan s and wa e s ess in ela ion o he amoun o usable pixels ha ing an in o ma i e
alue [
34
]. By ex ension, some expe s ha e [
35
] a gued ha using (NDVI) da a acqui ed
wi h an NOAA–Ad anced Ve y High Resolu ion Radiome e (AVHRR) enables co n p o-
duc ion o be p edic able a leas 2 mon hs be o e he ac ual ha es and a an accu acy
mul iple imes highe han ha o he wa e s ess p ocedu e. The e e enced a icle [
36
]
also emphasizes ha combining clima ological NDVI da a embodies a bene icial s ep o
inc ease he accu acy o he models; his assump ion is con i med wi hin s udy [
36
]. A
combina ion o me eo ological da a and sa elli e images o p edic abo eg ound biomass
and d y ma e con en s in B achia ia pas u es is ou lined in [37].
The accu acy o NDVI-de i ed co n yield p edic ions appa en ly depends on he scan
ime [
38
] and he olume o wa e in he plan du ing a ious pe iods o he day, ega dless
o he senso used [39,40].
A p edic ing app oach ha u ilizes he Lea a ea index (LAI) and es ima es he d y
ma e ia ield e lec ance measu emen s execu ed wi h mul ispec al sys ems (Landsa 8,
RapidEye) is desc ibed in s udy [41].
Fu he mo e, ega ding he p oblems ele an o he opic in gene al, se e al esea ch
epo s, a icles, and pape s discuss he ela ionship be ween he ege a ion indices and
nu i ional alues, [
42
,
43
]; he la e sou ce examines da a co ela ion be ween ege a ion
Remo e Sens. 2023,15, 3152 4 o 19
indices and he ni ogen nu i ion index (NNI), he in es iga ion being ocused solely on
peppe plan s. The ege a ion indices and he ag onomic pe o mance o co n a ie ies
unde di e en ni ogen a es a e compa ed in a icle [
44
]. Ou e o s concep ually ela e
especially o hose ou lined in epo [
45
], which p oposes an insigh in o he co ela ion
be ween canopy ege a ion and he g ow h indices o co n a ie ies wi h di e en ni ogen
e iciencies; he au ho s o [
45
], howe e , do no show conc e e ma hema ical exp essions
o inspec he ege a ion- o-nu i ional index ela ionships ha allow o he es ablishing
o he op imum co n ha es ime.
Ou a icle b oadly expands on he knowledge, esea ch, and applica ions a ailable
o da e. The ac ual no el y lies in he design o a new and mo e accu a e me hodology
(compa ed o, o ins ance, he solu ion adop ed in [
1
]) o de e mining he op imum
ha es ime by exploi ing he co ela ion be ween di e se ege a ion indices and he d y
ma e con en in a ious co n phenophases. Wi h such an inno a i e app oach, he a me
is no equi ed o sample he c op di ec ly in he ield and ha e i analyzed chemically, hus
sa ing a subs an ial amoun o ime and wo k. The de ini ion o he app op ia e ha es
ime leads o a scena io whe e he en i e p ocedu al chain is op imized, s a ing om he
seed plan ing and p oceeding h ough he ideal silage nu i ional alues o e en ually
secu e he maximum achie able yield in cow milk o biogas.
2. Ma e ials and Me hods
The da a collec ion and he ele an ma hema ical p ocessing a e cha ac e ized h ough
he block diag am and p esen a ion below. The le -hand po ion o Figu e 1A exposes
how a new equa ion is acqui ed ia u ilizing a eg ession model o he ege a ion indices
and a chemical analysis o he co n plan s; he igh -hand segmen (Figu e 1B), by con as ,
displays he use o an expe imen ally gene a ed equa ion o compu ing he d y ma e
wi hou ha ing o pe o m a chemical analysis. The d y ma e alue hen enables us o
es ablish he op imum ha es ime in he c op being in es iga ed.
Remo e Sens. 2023, 14, x FOR PEER REVIEW 4 o 20
Fu he mo e, ega ding he p oblems ele an o he opic in gene al, se e al esea ch
epo s, a icles, and pape s discuss he ela ionship be ween he ege a ion indices and
nu i ional alues, [42,43]; he la e sou ce examines da a co ela ion be ween ege a ion
indices and he ni ogen nu i ion index (NNI), he in es iga ion being ocused solely on
peppe plan s. The ege a ion indices and he ag onomic pe o mance o co n a ie ies
unde diffe en ni ogen a es a e compa ed in a icle [44]. Ou effo s concep ually ela e
especially o hose ou lined in epo [45], which p oposes an insigh in o he co ela ion
be ween canopy ege a ion and he g ow h indices o co n a ie ies wi h diffe en
ni ogen efficiencies; he au ho s o [45], howe e , do no show conc e e ma hema ical
exp essions o inspec he ege a ion- o-nu i ional index ela ionships ha allow o he
es ablishing o he op imum co n ha es ime.
Ou a icle b oadly expands on he knowledge, esea ch, and applica ions a ailable
o da e. The ac ual no el y lies in he design o a new and mo e accu a e me hodology
(compa ed o, o ins ance, he solu ion adop ed in [1]) o de e mining he op imum
ha es ime by exploi ing he co ela ion be ween di e se ege a ion indices and he d y
ma e con en in a ious co n phenophases. Wi h such an inno a i e app oach, he
a me is no equi ed o sample he c op di ec ly in he ield and ha e i analyzed
chemically, hus sa ing a subs an ial amoun o ime and wo k. The de ini ion o he
app op ia e ha es ime leads o a scena io whe e he en i e p ocedu al chain is
op imized, s a ing om he seed plan ing and p oceeding h ough he ideal silage
nu i ional alues o e en ually secu e he maximum achie able yield in cow milk o
biogas.
2. Ma e ials and Me hods
The da a collec ion and he ele an ma hema ical p ocessing a e cha ac e ized
h ough he block diag am and p esen a ion below. The le -hand po ion o Figu e 1A
exposes how a new equa ion is acqui ed ia u ilizing a eg ession model o he ege a ion
indices and a chemical analysis o he co n plan s; he igh -hand segmen (Figu e 1B), by
con as , displays he use o an expe imen ally gene a ed equa ion o compu ing he d y
ma e wi hou ha ing o pe o m a chemical analysis. The d y ma e alue hen enables
us o es ablish he op imum ha es ime in he c op being in es iga ed.
Figu e 1. A block diag am ou lining he ac ual speci ica ion, (A), and e i ica ion, (B), o he
ela ionships be ween he ege a ion indices and nu i ional alues in a ious ypes o co n hyb ids.
Figu e 1.
A block diag am ou lining he ac ual speci ica ion, (
A
), and e i ica ion, (
B
), o he ela ion-
ships be ween he ege a ion indices and nu i ional alues in a ious ypes o co n hyb ids.
2.1. Sensing Pe iods and Locali ies
The mul ispec al came a pho og amme ic imaging and he manual sampling we e
execu ed in co n ields a a ious spo s o he Sou h Mo a ian Region, Mo a ia, he Czech
Republic. The sampling ope a ions we e coo dina ed, e en hough he in e als sepa a ing
Remo e Sens. 2023,15, 3152 5 o 19
he indi idual s eps di e ed. The loca ions whe e samples we e collec ed o chemical
analysis we e eco ded in mul ispec al images (Figu e 2), and he p ese locali y selec ion
c i e ia had included ac o s such as su icien ege a ion he e ogenei y, soil composi ion,
and clima ic condi ions [
1
]. In esea ch yea 1, he sampling was ca ied ou nea he illage
o T oubsko om 23 July 2019 o 4 Sep embe 2019, a ou and i e di e se ime in e als
o plan phenophase in he silage and he g ain hyb ids, espec i ely.
Remo e Sens. 2023, 14, x FOR PEER REVIEW 5 o 20
2.1. Sensing Pe iods and Locali ies
The mul ispec al came a pho og amme ic imaging and he manual sampling we e
execu ed in co n ields a a ious spo s o he Sou h Mo a ian Region, Mo a ia, he Czech
Republic. The sampling ope a ions we e coo dina ed, e en hough he in e als
sepa a ing he indi idual s eps diffe ed. The loca ions whe e samples we e collec ed o
chemical analysis we e eco ded in mul ispec al images (Figu e 2), and he p ese locali y
selec ion c i e ia had included ac o s such as sufficien ege a ion he e ogenei y, soil
composi ion, and clima ic condi ions [1]. In esea ch yea 1, he sampling was ca ied ou
nea he illage o T oubsko om 23 July 2019 o 4 Sep embe 2019, a ou and i e di e se
ime in e als o plan phenophase in he silage and he g ain hyb ids, espec i ely.
(a) (b)
Figu e 2. (a) Visualizing he o e all a ea o he expe imen ; (b) posi ioning he co n ields ha we e
subjec ed o he pho og amme ic imaging in he ele an subsec o o he Sou h Mo a ian Region,
Mo a ia, Czech Republic.
In he pe iod om 12 Augus 2020 o 7 Oc obe 2020, he sampling was ca ied ou
be ween he municipali ies o Šlapanice and P ace (bo h in he B no coun y dis ic ). To
op imize and compa e he samples om he i s esea ch yea , we chose a highe
sampling equency, collec ing he i ems on 8 diffe en days. The same amoun o
sampling was alloca ed o he nex yea , when he expe imen s ook place in a ield nea
he own o Velké Pa lo ice (Břecla dis ic ). The samples comp ised wo co n hyb ids
and we e ga he ed om 2 Augus 2021 o 21 Sep embe 2021.
To es he alidi y o he co ela i e ela ionships and o con i m he hypo hesis ha
changes in he compu ed ege a ion indices a e p opo ional o a ia ions in he
nu i ional analysis, we conduc ed a sepa a e expe imen nea he illage o Knínice
(Blansko dis ic ), in ol ing 5 co n hyb ids on he day o hei ac ual ha es .
2.2. UAV Da a Collec ion and Analysis
The pho og amme ic da a o igina ed om a Micasence RedEdge-3 mul ispec al
came a moun ed on a DJI Ma ice 600 P o unmanned ae ial ehicle (Figu e 3). The
RedEdge de ice cap u es 5 diffe en bands (Table 1) and is i ed wi h a 3DR GPS module,
a downwelling ligh senso , E he ne , and o he in e aces.
Figu e 2.
(
a
) Visualizing he o e all a ea o he expe imen ; (
b
) posi ioning he co n ields ha we e
subjec ed o he pho og amme ic imaging in he ele an subsec o o he Sou h Mo a ian Region,
Mo a ia, Czech Republic.
In he pe iod om 12 Augus 2020 o 7 Oc obe 2020, he sampling was ca ied ou
be ween he municipali ies o Šlapanice and P ace (bo h in he B no coun y dis ic ). To
op imize and compa e he samples om he i s esea ch yea , we chose a highe sampling
equency, collec ing he i ems on 8 di e en days. The same amoun o sampling was
alloca ed o he nex yea , when he expe imen s ook place in a ield nea he own o Velké
Pa lo ice (Bˇ ecla dis ic ). The samples comp ised wo co n hyb ids and we e ga he ed
om 2 Augus 2021 o 21 Sep embe 2021.
To es he alidi y o he co ela i e ela ionships and o con i m he hypo hesis ha
changes in he compu ed ege a ion indices a e p opo ional o a ia ions in he nu i ional
analysis, we conduc ed a sepa a e expe imen nea he illage o Knínice (Blansko dis ic ),
in ol ing 5 co n hyb ids on he day o hei ac ual ha es .
2.2. UAV Da a Collec ion and Analysis
The pho og amme ic da a o igina ed om a Micasence RedEdge-3 mul ispec al
came a moun ed on a DJI Ma ice 600 P o unmanned ae ial ehicle (Figu e 3). The Red-
Edge de ice cap u es 5 di e en bands (Table 1) and is i ed wi h a 3DR GPS module, a
downwelling ligh senso , E he ne , and o he in e aces.
Be o e e alua ing he images, a su icien olume o he e ogeneous da a has o be
ob ained o allow me hods o be compa ed ha a e sui able o achie ing he bes possible
co ela ion wi h he nu i ional alues o he plan samples.
The imaging was pe o med along p e-p og ammed au oma ic ligh pa hs, each pa h
ha ing a p ecisely de ined, polygon-shaped scanning a ea wi hin he egion o in e es .
In he expe imen , we used he DJI au opilo and he Pix4D cap u e so wa e o plane he

Remo e Sens. 2023,15, 3152 6 o 19
pa h. The image p ocessing elied on S uc u e- om-Mo ion (SFM), a key pho og amme ic
echnique used o handle mul ispec al images ob ained om UAVs.
Remo e Sens. 2023, 14, x FOR PEER REVIEW 6 o 20
Figu e 3. Cap u ing he image da a wi h a d one-moun ed RedEdge came a.
Table 1. The pa ame e s o he RedEdge Micasense came a bands.
Band Numbe Band Colo Wa eleng h
[nm]
Bandwid h
[nm]
Calib a ion Panel
Re lec ance
1 Blue (B) 475 20 0.56
2 G een (G) 560 20 0.56
3 Red (R) 668 10 0.55
4 Nea in a ed
(NIR) 840 40 0.54
5 Red Edge (RE) 717 10 0.50
Be o e e alua ing he images, a sufficien olume o he e ogeneous da a has o be
ob ained o allow me hods o be compa ed ha a e sui able o achie ing he bes possible
co ela ion wi h he nu i ional alues o he plan samples.
The imaging was pe o med along p e-p og ammed au oma ic ligh pa hs, each
pa h ha ing a p ecisely de ined, polygon-shaped scanning a ea wi hin he egion o
in e es . In he expe imen , we used he DJI au opilo and he Pix4D cap u e so wa e o
plane he pa h. The image p ocessing elied on S uc u e- om-Mo ion (SFM), a key
pho og amme ic echnique used o handle mul ispec al images ob ained om UAVs.
The a ea co e ed o he es ing was small, meaning ha we assumed a ixed heigh ;
his heigh hen also cons i u ed he basis o he image compu a ion. In all o he h ee
esea ch yea s, he mapping co e ed a ec angula zone o 361 m × 362 m, i.e., an a ea o
app oxima ely 13.1 ha. The o al ligh pa h leng h eached 4.477 m. To scan he ull ange
o he in es iga ed sec o , a ligh las ed 31 min, wi h an o e lap o 70% be ween he
images. The UAV lew a a speed o 8.6 km/h and an al i ude o 40 m abo e he g ound.
In each o he spec al bands, we ook in a iably mo e han 330 images wi h a esolu ion
o 2.78 cm/pixel. The measu ed da a we e p ocessed wi h he Pix4D mappe a he use
Figu e 3. Cap u ing he image da a wi h a d one-moun ed RedEdge came a.
Table 1. The pa ame e s o he RedEdge Micasense came a bands.
Band Numbe Band Colo Wa eleng h [nm] Bandwid h [nm] Calib a ion Panel Re lec ance
1 Blue (B) 475 20 0.56
2 G een (G) 560 20 0.56
3 Red (R) 668 10 0.55
4
Nea in a ed(NIR)
840 40 0.54
5 Red Edge (RE) 717 10 0.50
The a ea co e ed o he es ing was small, meaning ha we assumed a ixed heigh ;
his heigh hen also cons i u ed he basis o he image compu a ion. In all o he h ee
esea ch yea s, he mapping co e ed a ec angula zone o 361 m
×
362 m, i.e., an a ea
o app oxima ely 13.1 ha. The o al ligh pa h leng h eached 4.477 m. To scan he ull
ange o he in es iga ed sec o , a ligh las ed 31 min, wi h an o e lap o 70% be ween he
images. The UAV lew a a speed o 8.6 km/h and an al i ude o 40 m abo e he g ound. In
each o he spec al bands, we ook in a iably mo e han 330 images wi h a esolu ion o
2.78 cm/pixel. The measu ed da a we e p ocessed wi h he Pix4D mappe a he use le el;
we did no es he image esolu ion changes o p ocessing ia a ious o he me hods.
The mul ispec al imaging deli e s ege a ion indices, which con ain in o ma ion
on di e en e lec ance alues o he elec omagne ic spec um ela ing o he biological
p ope ies o plan s. The mos widely used ege a ion indices a e hose whe e quan i a i e
indica o s, such as he olume o biomass wi hin an a ea, can be de e mined. A la ge
amoun o algo i hms o calcula e ege a ion indices a e a ailable, a ising om compu a ion
om a leas wo spec al images; he images a e selec ed in such a manne as o expose
ege a ion e lec ance changes, and in mos cases hey a e unc ionally equi alen . Mo e
han 150 ege a ion indices ha e been published in he li e a u e, bu only a small subse
ha e a s ong biophysical basis o ha e been sys ema ically es ed [46–48].
Remo e Sens. 2023,15, 3152 7 o 19
Each ege a ion index acks speci ic ege a ion cha ac e is ics and is con enien o
pa icula applica ions. Indices ha do no u ilize he nea -in a ed spec al band exhibi
limi ed (and limi ing) p ope ies and a e he e o e unsui able in p ac ical moni o ing o
ege a ion changes. To acili a e he analysis, we chose he a io indices NDVI,NDRE,
and GNDVI, all o which a e compu ed simila ly; hese ools, howe e , also con ain di -
e en spec al bands, and hus hey collec i ely o e a c oss-sec ion h ough impo an
wa eleng hs. Combining he indices hen yields applicable modi ica ions, whose da a a e
dissimila o hose deli e ed by he o iginally selec ed basic e sions [49].
Vege a ion indices a e no cons an , bu depend on sho - e m wea he changes and
he o e all amoun o sunligh . To e ine he esul s o he mul ispec al sensing, we need
o un calib a ion; his s ep is execu ed in a ious g owing seasons, unde di e se wea he
condi ions, and a he same phase o he day. Impo an ly, a da abase had o be o med
con aining he ou comes o se e al measu emen s, allowing us o choose he alues ha a e
achie able in op imum ci cums ances. Calib a ing he came a elimina es he inaccu acies
which s em om he use o one-o , single samples o he c ops, and c ea ing addi ional
images will acili a e compa ison o he indices.
2.2.1. NDVI (No malized Di e ence Vege a ion Index)
The NDVI is a nume ical indica o o plan heal h ha supplies da a on ege a ion
changes and, in a mo e de ailed sense, he amoun s o wa e s ess and chlo ophyll con-
ained in a plan . The index e alua es he moni o ed ege a ion su ace by using he a io
o he e lec ance o he ed and nea -in a ed pa s o he spec um [50].
The NDVI u ilizes he ed isible band, which is s ongly abso bed by he uppe
po ion o a plan ’s su ace, meaning ha he lowe le els do no signi ican ly con ibu e
o he NDVI measu emen . The co ela ion be ween he index and he plan ’s olume ic
p ope ies hus de e io a es; his is mo e p ominen in alle plan s wi h mul iple lea laye s
(such as co n a la e g ow h s ages) [51,52].
The e lec ance o he nea -in a ed spec um enables he index o easily dis inguish
sub le di e ences in ege a ion. In he ac ual sensing, he ac o s o majo impo ance
include shadows and he a mosphe e, whose impac leads o e lec ance changes wi hin
he di e en bands; he a mosphe ic e ec is eliminable ia co ec ion based on compa ing
images aken a a ious imes [49]. We ha e
NDVI =ρNIR −ρRed
ρNIR +ρRed
(1)
whe e
ρNIR
and
ρRed
deno e he e lec i i ies o he nea -in a ed and he ed wa eleng h
bands, espec i ely.
2.2.2. NDRE (No malized Di e ence Red Edge Index)
Simila o he abo e-cha ac e ized ool, he NDRE exploi s he nea -in a ed spec um
and he equency band ha lies in he ansi ion egion sepa a ing he isible and he
in a ed spec a, i.e., he ed edge; we ha e
NDRE =ρNIR −ρRedEdge
ρNIR +ρRedEdge
. (2)
2.2.3. GNDVI (G een No malized Di e ence Vege a ion Index)
This me hod employs he g een spec um wa eleng hs a he han he ed ones; hese
a e
ρNIR
and
ρG een
, deno ing he e lec ance alues in he nea -in a ed and he g een bands,
espec i ely [53,54]. We ha e
GNDVI =ρNIR −ρG een
ρNIR +ρG een
. (3)
Remo e Sens. 2023,15, 3152 8 o 19
2.3. Chemical Analysis o he Samples Ob ained om Field-Ga he ed Co n Plan s
To ob ain he nu i ional pa ame e s o he ield samples o co n, we ca ied ou a
dedica ed labo a o y chemical analysis. The ege a ion indices and he ou comes o he
analysis we e hen co ela ed a a ious phenological g ow h s ages o he moni o ed c ops
o es ablish he ideal ha es ime as ega ds he co n yield o silage making and animal
eed on he one hand, and me hane p oduc ion in biogas plan s on he o he .
The sampling was in a iably pe o med a iden ical ime in e als, oge he wi h he
mul ispec al imaging. To su ey he quali y o he co n hyb id, we op ed o sampling
acco ding o he me hodology ecommended by he Cen al Ins i u e o Supe ising and
Tes ing in Ag icul u e, B no, Mo a ia, he Czech Republic [
55
]. The samples we e acqui ed
om h ee di e en sec o s o expose he local ield g ow h homogenei y; in each o he
cases, we ook a ow o 10 whole co n plan s and ma ked hei posi ions on he mul ispec al
maps acqui ed o e he a eas speci ied in Figu e 2.
Subsequen ly, we modi ied and analyzed he plan s o de e mine he majo quan i ies,
namely, he FM—F esh ma e ( esh weigh )—and EW—Ea weigh . In gene al e ms,
he analysis also enables he ollowing nu i ional alues o be es ablished: he DM–d y
ma e , meaning he d y ma e olume– om which we hen de ine he alues o CP–c ude
p o ein (ni ogenous compounds); CF—c ude ibe (c ude ibe ); s a ch (s a ch con en ); ash
(ash p esence); NDF—neu al de e gen ibe (neu al de e gen ibe ); DNDF—diges ibili y
NDF (neu al de e gen ibe diges ibili y a e); and DOM—diges ibili y o ganic ma e
(o ganic ma e diges ibili y a e). The analyzed da a e en ually allow us o calcula e he
yield pe hec a e, comp ising he YFM—yield o esh ma e ( esh ma e sha e indica o )
and YDM—yield o d y ma e (d y ma e sha e indica o ); in o al, a hec a e is assumed
o p oduce 80,000 co n plan s.
2.4. Da a Co ela ion
To de ine he ela ionships be ween he esul s acqui ed wi h he nu i ional analysis on
he one hand (Nu ) and he alues o he ege a ion indices (Veg) on he o he , we calcula ed
he ege a ion index alues
Nu ,Veg
acco ding o Pea son’s co ela ion coe icien . The
deg ee o co ela ion is speci ied by he compu ed co ela ion coe icien , which can ake
alues om
−
1 o +1. The e minal alues o he coe icien +1 ep esen a comple ely di ec
ela ionship, and he i s a iable ends o inc ease; by con as , he alues o he coe icien
−
1 ep esen a ully in e se ela ionship, and he i s a iable ends o dec ease. I he
co ela ion coe icien equals ze o, he e is no linea ela ionship be ween he pa ame e
being moni o ed and he e lec ance o ege a ion index. We ha e
Nu ,Veg =
1
n∑n
i=1Nu i−VegVegi−Nu 
SNu ·SVeg
(4)
SNu =s1
n
n
∑
i=1Nu i2−Nu 2, (5)
SVeg =s1
n
n
∑
i=1Vegi2−Veg2, (6)
whe e
Nu
ep esen s he nu i ion analysis alue,
Veg
deno es he ege a ion index alue,
Veg and Nu s and o he sample means, and SVeg and SNu a e he s anda d de ia ions.
The quan i y
R2
indica es he coe icien o de e mina ion. I akes alues om 0 o 1,
was compu ed o exp ess he join a iabili y o he a iables, and speci ies he quali y o
he eg ession model. A alue o 1 means pe ec p edic ion o he alues o he dependen
a iable, while a alue o 0 signi ies minimum in o ma ion ela ing o he knowledge o he
dependen a iable. The coe icien was compu ed by using he ela ionships below.
Remo e Sens. 2023,15, 3152 9 o 19
A da ase has n alues ma ked as y
1
,
. . .
,y
n
(collec i ely known as y
i
o a ec o
y
= [y
1
,
. . .
,y]
nT
), each associa ed wi h a i ed (o modeled, p edic ed) alue
1
,
. . .
,
n
(deno ed by i).
I yis he mean o he obse ed da a,
y=1
n
n
∑
i=1
yi, (7)
hen he da ase a iabili y can be measu ed wi h wo sums-o -squa es o mulas. Fi s , le
us no e he sum o he squa es o esiduals, also called he esidual sum o squa es:
SS es =∑
i
(yi− i)2. (8)
The la e equa ion embodies he o al sum o squa es (p opo ional o he da a a i-
ance), eading
SS o =∑
i
(yi−y)2. (9)
The mos gene al de ini ion o he coe icien o de e mina ion is
R2=1−SS es
SS o . (10)
In he bes case, he modeled alues exac ly ma ch he obse ed ones, esul ing in
SS es =
0 and
R2=
1. A baseline model, which always p edic s
y
, will ha e
R2=
0; models
ha deli e p edic ions wo se han he baseline will assume a nega i e R2[56].
To ob ain ano he pa ame e o de e mining whe he he co ela ion coe icien s
ake a alue ha e ec i ely implies an in e -coe icien ela ionship, we compu ed hei
s a is ical signi icance.
The s a is ically signi ican a e was es ablished by using a con inuous p obabili y
dis ibu ion based on S uden ’s concep ( -dis ibu ion); we ha e
sco e = ( Nu ,Veg·pn−2)
q1− Nu ,Veg2), (11)
whe e nis he amoun o he obse ed co ela ion phases.
When seeking a s a is ically ele an alue, we selec ed a signi icance le el o 2%,
co esponding o a qua ile o 99%. The -dis ibu ion alues o se en, ou , and h ee
deg ees o eedom equal 2.998, 3.747, and 4.541, espec i ely. I he co ela ion coe icien
exceeds he c i ical alue, he co ela ion can be conside ed s a is ically ele an .
2.5. Me hod o Ve i y he Resul ing Equa ions: A Sepa a e Co n Field
The equa ions de ining he linea ela ionship o he d y ma e alues o he co ela ed
ege a ion indices NDVI,NDRE, and GNDVI we e alida ed agains he ou comes o a
single-sho expe imen o 5 hyb ids ( he ES Joke , ES Welling on, KTG Ka laxx, Absolu is-
simo, and Rudol inio) on he day o hei ac ual ha es . The d y ma e con en p edic ions
co e ed hyb ids g own o g ain, wi h he ideal ha es window shi ed o alues be ween
380 g/kg and 420 g/kg.
In each o hese hyb ids, he in e ac ion o he acqui ed ela ionships (14)–(16) was
se down and e i ied. Using nu i ional analysis, we de e mined he d y ma e olume
in he whole plan s, and his quan i y was deno ed as he d y ma e con en ional ue
alue,
DMCTV
. Subsequen ly, we applied he ege a ion indices o compu e he p edic ed
d y ma e alue,
DMPV
, and es ablished he absolu e and ela i e de ia ions,
∆DM
and
Remo e Sens. 2023,15, 3152 16 o 19
4.5. Compa ing he Resul s
This a icle de elops he ou comes o s udy [
1
], connec ing hem wi h no el esea ch
and ou lining a mo e comp ehensi e app oach o he p oblem. While he e e enced
sou ce [
1
] e alua es one co n hyb id in one season, he p esen a icle discusses he ela ion-
ship be ween he d y ma e and he ege a ion indices o e da a collec ed du ing h ee
yea s, con i ming ha he esul s a e alid o no me ely a single hyb id, bu gene ally. In
con as , no s a is ically signi ican ela ionship o he CF has been shown, and he s a ch
alue appea ed o be ele an only in he NDVI.
A icle [
20
] examines eg ession models o es ima ing c op yield ia he NDVI and
measu emen s o ela i e c op yields (paddy ice, win e whea , and co n); he au ho s ec-
ommend using he models especially in a eas whe e he c op ypes a e no exac ly known.
In epo [
41
], he d y ma e alue was con i med ia ield e lec ance measu emen s
execu ed wi h mul ispec al sys ems (Landsa 8, RapidEye). By compa ison, ou app oach,
when con on ed wi h he sa elli e image-based da a acquisi ion, o e s he ad an age o a
highe esolu ion in he imaging and map o ming, and his capabili y hen ensu es be e
da a accu acy.
The esul s o he expe imen he ein con i m he ege a ion- o-nu i ional index da a
co ela ion de ailed elsewhe e, especially in he e e enced sou ce [
45
]. The cen al asse
o ou a icle ne e heless lies in he speci ied ma hema ical ela ionships be ween he
ege a ion and he nu i ional indices; hese ins umen s, impo an ly, acili a e de e mining
he d y ma e alue om an en i e ield and hus op imizing he ha es ime.
4.6. Limi a ions o he App oach
The p oposed me hod o UAV mul ispec al came a ield scanning and ege a ion-index-
based d y ma e compu a ion includes unce ain ies; hese unce ain ies es in he quali y
o he mul ispec al senso and also i s calib a ion o sui he season and en i onmen .
The epea abili y o he p ocedu e depends on he wea he condi ions, as he ope a ion
o an unmanned ae ial ehicle is a ec ed by ain, wind, and loca ion o he c ops o be
moni o ed ( o example, in a d one ligh es ic ion zone). A majo disad an age is he
limi ed ange o an UAV: O e a eas la ge han 200 ha, imaging wi h his me hod becomes
challenging due o he ba e y capaci y. Al e na i ely, ixed-wing UAVs may be employed
because hey p o ide a longe ange pe ba e y (~50 min); he eBee X, howe e , deli e s
up o 90 min. Using a d one is e ec i e only o la ge ege a ion uni s.
5. Conclusions
Analyzing mul ispec al images by using p ecise knowledge o c op heal h is one o
he p ocesses ha suppo s he ansi ion om adi ional a ming o p ecision ag icul u e.
Inc easing he quali y o ha es ed co n and educing he eed c op consump ion by
de e mining he co ec ha es ime will p oduce an inno a i e app oach, namely, non-
con ac analysis o he plan a di e en s ages o g ow h; his echnique will o e a po en ial
o au oma ed and apidly scalable applica ion in mos ypes o cul i a ed ege a ion. In
co n, he app op ia e ha es ime is es ablished om he amoun o d y ma e , depending
on whe he he chopped plan s a e o be ensiled o odde o used as me hane p oduc ion
ma e ial in a biogas plan . Thus, up- o-da e, accu a e knowledge o he nu i ional alues,
ideally collec ed ac oss he c op ield, embodies an essen ial ac o in selec ing he igh
ime window.
Such goals and asks can be e ec i ely pe o med by means o emo e sensing wi h a
UAV-moun ed mul ispec al came a and ia he equa ions se ou in Figu e 4. The discussed
me hod elimina es he need o chemical analysis o samples collec ed om only a ew
loca ions in a la ge ield ha suppo s he e ogeneous ege a ion. Speci ying he op imum
ha es pe iod is assigned conside able ecological and economic impo ance, especially i
ela ed o he en i e p ocessing chain; The au ho s p oceed om op imum co n ha es ing
based on he p e-de e mined olume o d y ma e o me hane p oduc ion in biogas plan s,
espec ing also he links be ween eed c op and cow milk.

Remo e Sens. 2023,15, 3152 17 o 19
The ege a ion ela ionship g aphs in Figu e 4lead o equa ions ha ind use in p e-
dic ing he op imum ha es ime ia d y ma e alues. E alua ing he in o ma ion om
he abo e chap e s, we can conclude ha he g ea es p edic ion ele ance is embedded in
Equa ion (16), which de ines he ela ionship be ween he GNDVI and d y ma e . Resul s
cha ac e izable as e y good bu somewha in e io o hose ob ained o he GNDVI we e
ound in he NDVI–d y ma e ela ionship (15). The GNDVI and NDVI alues also allow
o es ima ing he yield cha ac e is ics, such as he YFM and YDM.
In iew o he e y s ong co ela ion be ween he GNDVI and d y ma e con en
alues, he GNDVI can be desc ibed as ha ing he bes p edic ion esul s in he linea model.
The main bene i s o he me hod include he gene al alidi y o he ela ionships
be ween he ege a ion indices and he d y ma e o di e en co n hyb ids. Con e sely, a
cen al disad an age lies in he sensi i i y o clima ic condi ions; The sensing is no easible
du ing ain o hea y winds.
Au ho Con ibu ions:
Concep ualiza ion, J.J. and V.J.; me hodology, J.J. V.J. and P.M.; da a cu a ion,
J.J., V.J. and H.S.; w i ing—o iginal d a p epa a ion, J.J., V.J., P.M., H.S. and P.D.; unding acquisi ion,
P.R. All au ho s ha e ead and ag eed o he published e sion o he manusc ip .
Funding:
This pape was unded om he gene al s uden de elopmen p ojec a B no Uni e si y
o Technology.
Da a A ailabili y S a emen :
The da a p esen ed in his s udy a e a ailable on eques om he
co esponding au ho .
Con lic s o In e es : The au ho s decla e no con lic o in e es .
Re e ences
1.
Janoušek, J.; Jambo , V.; Ma coˇn, P.; Dohnal, P.; Synko á, H.; Fiala, P. Using UAV-Based Pho og amme y o Ob ain Co ela ion
be ween he Vege a ion Indices and Chemical Analysis o Ag icul u al C ops. Remo e Sens. 2021,13, 1878. [C ossRe ]
2.
Minaˇ ík, R.; Langhamme , J.; Lendzioch, T. De ec ion o Ba k Bee le Dis u bance a T ee Le el Using UAS Mul ispec al Image y
and Deep Lea ning. Remo e Sens. 2021,13, 4768. [C ossRe ]
3.
Ve eka , N.T.; Gad, R.S.; Fe nandes, I.; Pa ab, J.S.; Desai, A.R.; Pawa , J.D.; Naik, G.M.; Umapa hy, S. Non-in asi e hype spec al
imaging app oach o ui quali y con ol applica ion and classi ica ion: Case s udy o apple, chikoo, gua a ui s. J. Food Sci.
Technol. 2015,52, 6978–6989. [C ossRe ]
4.
Pa k, B.; Law ence, K.C.; Windham, W.R.; Smi h, D.P. Mul ispec al imaging sys em o ecal and iges a de ec ion on poul y
ca casses. J. Food P ocess Eng. 2004,27, 311–327. [C ossRe ]
5.
Cen, H.; Lu, R.; Zhu, Q.; Mendoza, F. Nondes uc i e de ec ion o chilling inju y in cucumbe ui using hype spec al imaging
wi h ea u e selec ion and supe ised classi ica ion. Pos ha es Biol. Technol. 2016,111, 352–361. [C ossRe ]
6.
Lleó, L.; Ba ei o, P.; Ruiz-Al isen , M.; He e o, A. Mul ispec al images o peach ela ed o i mness and ma u i y a ha es .
J. Food Eng. 2009,93, 229–235. [C ossRe ]
7.
Zhang, H.; Paliwal, J.; Jayas, D.S.; Whi e, N.D.G. Classi ica ion o Fungal In ec ed Whea Ke nels Using Nea -In a ed Re lec ance
Hype spec al Imaging and Suppo Vec o Machine. T ans. ASABE Am. Soc. Ag ic. Biol. Eng. 2007,50, 1779–1785. [C ossRe ]
8.
Lukas, V.; Huˇnady, I.; Kin l, A.; Meze a, J.; Hamme schmied , T.; Sobo ko á, J.; B nický, M.; Elbl, J. Using UAV o Iden i y he
Op imal Vege a ion Index o Yield P edic ion o Oil Seed Rape (B assica napus L.) a he Flowe ing S age. Remo e Sens.
2022
,
14, 4953. [C ossRe ]
9.
Du ko á, R.; Poláko á, L.; Lukas, V.; Fuˇcík, P. The E ec o Con olled Tile D ainage on G ow h and G ain Yield o Sp ing Ba ley
as De ec ed by UAV Images, Yield Map and Soil Mois u e Con en . Remo e Sens. 2022,14, 4959. [C ossRe ]
10.
G acia-Rome o, A.; Ve ga a-Díaz, O.; Thie elde , C.; Cai ns, J.E.; Ke au e , S.C.; A aus, J.L. Pheno yping Conse a ion Ag icul u e
Managemen E ec s on G ound and Ae ial Remo e Sensing Assessmen s o Maize Hyb id Pe o mance in Zimbabwe. P oceedings
2018,2, 7. [C ossRe ]
11.
Yang, B.; Zhu, W.; Rezaei, E.E.; Li, J.; Sun, Z.; Zhang, J. The Op imal Phenological Phase o Maize o Yield P edic ion wi h
High-F equency UAV Remo e Sensing. Remo e Sens. 2022,14, 1559. [C ossRe ]
12.
Ma ese, A.; Toscano, P.; Genna o, S.F.; Genesio, L.; Vacca i, F.P.; P imice io, J.; Belli, C.; Zaldei, A.; Bianconi, R.; Gioli, B.
In e compa ison o UAV, ai c a and sa elli e emo e sensing pla o ms o p ecision i icul u e. Remo e Sens.
2015
,7, 2971–2990.
[C ossRe ]
13.
Kuma , A.; Desai, S.V.; Balasub amanian, V.N.; Rajalakshmi, P.; Guo, W.; Naik, B.B.; Bal am, M.; Desai, U.B. E icien Maize
Tassel-De ec ion Me hod using UAV based emo e sensing. Remo e Sens. Appl. Soc. En i on. 2021,23, 100549. [C ossRe ]
14.
Yao, H.; Qin, R.; Chen, X. Unmanned Ae ial Vehicle o Remo e Sensing Applica ions—A Re iew. Remo e Sens.
2019
,11, 1443.
[C ossRe ]
Remo e Sens. 2023,15, 3152 18 o 19
15.
Su, W.; Zhang, M.; Bian, D.; Liu, Z.; Huang, J.; Wang, W.; Wu, J.; Guo, H. Pheno yping o Co n Plan s Using Unmanned Ae ial
Vehicle (UAV) Images. Remo e Sens. 2019,11, 2021. [C ossRe ]
16.
Lei, L.; Qiu, C.; Li, Z.; Han, D.; Han, L.; Zhu, Y.; Wu, J.; Xu, B.; Feng, H.; Yang, H.; e al. E ec o Lea Occlusion on Lea A ea
Index In e sion o Maize Using UAV–LiDAR Da a. Remo e Sens. 2019,11, 1067. [C ossRe ]
17.
Louis, J.; P lug, B.; Main-Kno n, M.; Debaecke , V.; Muelle -Wilm, U.; Iannone, R.Q.; Cadau, E.G.; Boccia, V.; Gascon, F.
Sen inel-2 Global Su ace Re lec ance Le el-2a P oduc Gene a ed wi h Sen2Co . In P oceedings o he IGARSS 2019—2019 IEEE
In e na ional Geoscience and Remo e Sensing Symposium, Yokohama, Japan, 28 July–2 Augus 2019; pp. 8522–8525. [C ossRe ]
18.
D usch, M.; Del Bello, U.; Ca lie , S.; Colin, O.; Fe nandez, V.; Gascon, F.; Hoe sch, B.; Isola, C.; Labe in i, P.; Ma imo , P.;
e al. Sen inel-2: ESA’s Op ical High-Resolu ion Mission o GMES Ope a ional Se ices. Remo e Sens. En i on.
2012
,120, 25–36.
[C ossRe ]
19.
Islam, M.R.; Ga cia, S.C. P edic ion o D y Ma e Yield o Hyb id Fo age Co n G own o Silage. C op Sci.
2014
,54, 2362–2372.
[C ossRe ]
20.
Huang, J.; Wang, H.; Dai, Q.; Han, D. Analysis o NDVI Da a o C op Iden i ica ion and Yield Es ima ion. IEEE J. Sel. Top. Appl.
Ea h Obs. Remo e Sens. 2014,7, 4374–4384. [C ossRe ]
21.
Wang, J.; Rich, P.M.; P ice, K.P.; Ke le, W.D. Rela ionships be ween NDVI, G assland P oduc ion, and C op Yield in he Cen al
G ea Plains. Geoca o In . 2005,20, 5–11. [C ossRe ]
22.
Cab e a-Bosque , L.; Mole o, G.; S ellacci, A.; Bo , J.; Nogués, S.; A aus, J. NDVI as a po en ial ool o p edic ing biomass, plan
ni ogen con en and g ow h in whea geno ypes subjec ed o di e en wa e and ni ogen condi ions. Ce eal Res. Commun.
2011
,
39, 147–159. [C ossRe ]
23.
Sakamo o, T.; Gi elson, A.A.; A kebaue , T.J. Nea eal- ime p edic ion o U.S. co n yields based on ime-se ies MODIS da a.
Remo e Sens. En i on. 2014,147, 219–231. [C ossRe ]
24.
Ines, A.V.; Das, N.N.; Hansen, J.W.; Njoku, E.G. Assimila ion o emo ely sensed soil mois u e and ege a ion wi h a c op
simula ion model o maize yield p edic ion. Remo e Sens. En i on. 2013,138, 149–164. [C ossRe ]
25.
Johnson, D.M. An assessmen o p e- and in-season emo ely sensed a iables o o ecas ing co n and soybean yields in he
Uni ed S a es. Remo e Sens. En i on. 2014,141, 116–128. [C ossRe ]
26.
Ma, Y.; Zhang, Z.; Kang, Y.; Özdo˘gan, M. Co n yield p edic ion and unce ain y analysis based on emo ely sensed a iables
using a Bayesian neu al ne wo k app oach. Remo e Sens. En i on. 2021,259, 112408. [C ossRe ]
27.
de Oli ei a, M.F.; O iz, B.V.; Mo a a, G.T.; Jiménez, A.-F.; Rolim, G.D.S.; da Sil a, R.P. T aining Machine Lea ning Algo i hms
Using Remo e Sensing and Topog aphic Indices o Co n Yield P edic ion. Remo e Sens. 2022,14, 6171. [C ossRe ]
28.
Tang, Z.; Guo, J.; Xiang, Y.; Lu, X.; Wang, Q.; Wang, H.; Cheng, M.; Wang, H.; Wang, X.; An, J.; e al. Es ima ion o Lea A ea Index
and Abo e-G ound Biomass o Win e Whea Based on Op imal Spec al Index. Ag onomy 2022,12, 1729. [C ossRe ]
29. Mu uganan ham, P.; Wibowo, S.; G andhi, S.; Sam a , N.H.; Islam, N. A Sys ema ic Li e a u e Re iew on C op Yield P edic ion
wi h Deep Lea ning and Remo e Sensing. Remo e Sens. 2022,14, 1990. [C ossRe ]
30.
an Klompenbu g, T.; Kassahun, A.; Ca al, C. C op Yield P edic ion Using Machine Lea ning: A Sys ema ic Li e a u e Re iew.
Compu . Elec on. Ag ic. 2020,177, 105709. [C ossRe ]
31.
Khalil, Z.H.; Abdullae , S.M. Neu al Ne wo k o G ain Yield P edic ing Based Mul ispec al Sa elli e Image y: Compa a i e
S udy. P ocedia Compu . Sci. 2021,186, 269–278. [C ossRe ]
32.
Pan , J.; Pan , R.P.; Kuma Singh, M.; P a ap Singh, D.; Pan , H. Analysis o Ag icul u al C op Yield P edic ion Using S a is ical
Techniques o Machine Lea ning. Ma e . Today P oc. 2021,46, 10922–10926. [C ossRe ]
33.
Ilyas, Q.; Ahmad, M.; Mehmood, A. Au oma ed Es ima ion o C op Yield Using A i icial In elligence and Remo e Sensing
Technologies. Bioenginee ing 2023,10, 125. [C ossRe ]
34.
Wang, R.; Che kaue , K.; Bowling, L. Co n Response o Clima e S ess De ec ed wi h Sa elli e-Based NDVI Time Se ies. Remo e
Sens. 2016,8, 269. [C ossRe ]
35.
Mkhabela, M.S.; Mkhabela, M.S.; Mashinini, N.N. Ea ly maize yield o ecas ing in he ou ag o-ecological egions o Swaziland
using NDVI da a de i ed om NOAA’s-AVHRR. Ag ic. Fo . Me eo ol. 2005,129, 1–9. [C ossRe ]
36.
Coelho, A.P.; Rosalen, D.L.; Fa ia, R.T. Vege a ion indices in he p edic ion o biomass and g ain yield o whi e oa unde i iga ion
le els. T op. Ag ic. Res. 2018,48, 109–117. [C ossRe ]
37.
B e as, I.L.; Valen e, D.S.; Sil a, F.F.; Chizzo i, M.L.; Paulino, M.F.; D’áu ea, A.P.; Paciullo, D.S.; Ped ei a, B.C.; Chizzo i, F.H.
P edic ion o abo eg ound biomass and d y-ma e con en in B achia ia pas u es by combining me eo ological da a and sa elli e
image y. G ass Fo age Sci. 2021,76, 340–352. [C ossRe ]
38.
S o wa, E.; Masuka, J.A.; Maasdo p, B.; Mu wi a, A. Spec al Indices: In-Season D y Mass and Yield Rela ionship o Flue-Cu ed
Tobacco unde Di e en Plan ing Da es and Fe ilise Le els. In . Sch. Res. No . 2013,2013, 816767. [C ossRe ]
39.
Ma esma, A.; Chambe lain, L.; Taga akis, A.; Kha el, T.; Godwin, G.; Czymmek, K.J.; Shields, E.; Ke e ings, Q.M. Accu acy o
NDVI-de i ed co n yield p edic ions is impac ed by ime o sensing. Compu . Elec on. Ag ic. 2020,169, 105236. [C ossRe ]
40.
Rahe lah, B.V.; Salgado, P.; And iana isoa, B.; Tilla d, E.; Raza ind azaka, H.; Le Mezo, L.; Ramalanjaona, V.L. Rela ionship
be ween no malized di e ence ege a ion index (NDVI) and o age biomass yield in he Vakinanka a a egion, Madagasca .
Li es . Res. Ru al. De . 2014,26, 1–11.
41.
Ge ighausen, H.; Lilien hal, H.; Ja me , T.; Siegmann, B. E alua ion o lea a ea index and d y ma e p edic ions o c op g ow h
modelling and yield es ima ion based on ield e lec ance measu emen s. eARSeL eP oceedings 2016,14, 71–90.
Remo e Sens. 2023,15, 3152 19 o 19
42.
Junio , A.S.D.A.; Melo, F.D.B.; Bas os, E.A.; Ca doso, M.J. E alua ion o The Nu i ional S a us o Co n by Vege a ion Indices Via
Ae ial Images. Ciência Ru al 2021,51, 1–13. [C ossRe ]
43.
de Souza, R.; Peña-Flei as, M.T.; Thompson, R.B.; Galla do, M.; Padilla, F.M. Assessing Pe o mance o Vege a ion Indices o
Es ima e Ni ogen Nu i ion Index in Peppe . Remo e Sens. 2020,12, 763. [C ossRe ]
44.
Flo es, M.D.S.; Paschoale e, W.M.; Baio, F.H.R.; Campos, C.N.S.; Pan aleão, A.D.A.; Teodo o, L.P.R.; Júnio , C.A.D.S.; Teodo o, P.E.
Rela ionship be ween Vege a ion Indices and Ag onomic Pe o mance o Maize Va ie ies unde Di e en Ni ogen Ra es. Biosci. J.
2020,36, 1638–1644. [C ossRe ]
45.
Zhao, X.; Wang, S.L.; Wen, T.; Xu, J.; Huang, B.; Yan, S.; Gao, G.; Zhao, Y.; Li, H.; Qiao, J.; e al. On Co ela ion be ween Canopy
Vege a ion and G ow h Indexes o Maize Va ie ies wi h Di e en Ni ogen E iciencies. Open Li e Sci.
2023
,18, 1–12. [C ossRe ]
[PubMed]
46.
Janse, P.V.; Deshmukh, R.R.; Randi e, P.U. Vege a ion Indices o C op Managemen : A Re iew. In . J. Res. Anal. Re . IJRAR
2019
,
6, 1–4.
47.
P ice, J. Lea a ea index es ima ion om isible and nea -in a ed e lec ance da a. Remo e Sens. En i on.
1995
,52, 55–65.
[C ossRe ]
48.
Panda, S.S.; Ames, D.P.; Panig ahi, S. Applica ion o Vege a ion Indices o Ag icul u al C op Yield P edic ion Using Neu al
Ne wo k Techniques. Remo e Sens. 2010,2, 673–696. [C ossRe ]
49.
Xue, J.; Su, B. Signi ican Remo e Sensing Vege a ion Indices: A Re iew o De elopmen s and Applica ions. J. Sens.
2017
,
2017, 1353691. [C ossRe ]
50.
Buma, W.G.; Lee, S.-I. Mul ispec al Image-Based Es ima ion o D ough Pa e ns and In ensi y a ound Lake Chad, A ica. Remo e
Sens. 2019,11, 21. [C ossRe ]
51.
Co igan, F. Mul ispec al Imaging Came a D ones in Fa ming Yield Big Bene i s. D oneZon, 2020. A ailable online: h ps://www.
d onezon.com/lea n-abou -d ones-quadcop e s/mul ispec al-senso -d ones-in- a ming-yield-big-bene i s/(accessed on 22
Ma ch 2020).
52.
Camma ano, D.; Fi zge ald, G.; Basso, B.; O’Lea y, G.; Chen, D.; G ace, P.; Fio en ino, C. Use o he Canopy Chlo ophyll Con en
Index (CCCI) o Remo e Es ima ion o Whea Ni ogen Con en in Rain ed En i onmen s. Ag on. J.
2011
,103, 1597–1603.
[C ossRe ]
53.
Bausch, W.C.; Hal o son, A.D.; Cip a, J. Quickbi d sa elli e and g ound-based mul ispec al da a co ela ions wi h ag onomic
pa ame e s o i iga ed maize g own in small plo s. Biosys . Eng. 2008,101, 306–315. [C ossRe ]
54.
Gi elson, A.A.; Me zlyak, M.N. Remo e sensing o chlo ophyll concen a ion in highe plan lea es. Ad . Space Res.
1998
,
22, 689–692. [C ossRe ]
55.
ÚKZÚZ. Me hods o Plan Va ie y S a e Tes s CISTA, Pu suan o he Valid Wo ding om he Yea 1999;ÚKZÚZ: B no, Czech
Republic, 1999.
56. Achen, C.H. Wha Does “Explained Va iance” Explain? A Reply. Poli ical Anal. 1990,2, 173–184. [C ossRe ]
Disclaime /Publishe ’s No e:
The s a emen s, opinions and da a con ained in all publica ions a e solely hose o he indi idual
au ho (s) and con ibu o (s) and no o MDPI and/o he edi o (s). MDPI and/o he edi o (s) disclaim esponsibili y o any inju y o
people o p ope y esul ing om any ideas, me hods, ins uc ions o p oduc s e e ed o in he con en .