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Repeatable semantic reef-mapping through photogrammetry and label-augmentation

Abstract

In an endeavor to study natural systems at multiple spatial and taxonomic resolutions, there is an urgent need for automated, high-throughput frameworks that can handle plethora of information. The coalescence of remote-sensing, computer-vision, and deep-learning elicits a new era in ecological research. However, in complex systems, such as marine-benthic habitats, key ecological processes still remain enigmatic due to the lack of cross-scale automated approaches (mms to kms) for community structure analysis. We address this gap by working towards scalable and comprehensive photogrammetric surveys, tackling the profound challenges of full semantic segmentation and 3D grid definition. Full semantic segmentation (where every pixel is classified) is extremely labour-intensive and difficult to achieve using manual labeling. We propose using label-augmentation, i.e., propagation of sparse manual labels, to accelerate the task of full segmentation of photomosaics. Photomosaics are synthetic images generated from a projected point-of-view of a 3D model. In the lack of navigation sensors (e.g., a diver-held camera), it is difficult to repeatably determine the slope-angle of a 3D map. We show this is especially important in complex topographical settings, prevalent in coral-reefs. Specifically, we evaluate our approach on benthic habitats, in three different environments in the challenging underwater domain. Our approach for label-augmentation shows human-level accuracy in full segmentation of photomosaics using labeling as sparse as 0.1%, evaluated on several ecological measures. Moreover, we found that grid definition using a leveler improves the consistency in community-metrics obtained due to occlusions and topology (angle and distance between objects), and that we were able to standardise the 3D transformation with two percent error in size measurements. By significantly easing the annotation process for full segmentation and standardizing the 3D grid definition we present a semantic mapping methodology enabling change-detection, which is practical, swift, and cost-effective. Our workflow enables repeatable surveys without permanent markers and specialized mapping gear, useful for research and monitoring, and our code is available online. Additionally, we release the Benthos data-set, fully manually labeled photomosaics from three oceanic environments with over 4500 segmented objects useful for research in computer-vision and marine ecology. Yuval, M.; Alonso, I.; Eyal, G.; Tchernov, D.; Loya, Y.; Murillo, A.C.; Treibitz, T.

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Repeatable semantic reef-mapping through photogrammetry and label-augmentation

Author: Yuval, M.; Loya, Y.; Treibitz, T.; Murillo, A.C.; Tchernov, D.; Eyal, G.; Alonso, I.
Year: 2021
DOI: 10.3390/rs13040659
Source: https://zaguan.unizar.es/record/99714/files/texto_completo.pdf
emo e sensing
A icle
Repea able Seman ic Ree -Mapping h ough Pho og amme y
and Label-Augmen a ion
Ma an Yu al 1,2,*,† , Iñigo Alonso 3, Gal Eyal 4,5 , Dan Tche no 2, Yossi Loya 6,
Ana C. Mu illo 3and Tali T eibi z 1


Ci a ion: Yu al, M.; Alonso, I.; Eyal,
G.; Tche no , D.; Loya, Y.; Mu illo,
A.C.; T eibi z, T. Repea able Seman ic
Ree -Mapping h ough
Pho og amme y and
Label-Augmen a ion. Remo e Sens.
2021,13, 659. h ps://doi.o g/
10.3390/ s13040659
Academic Edi o : John Bu ns
Recei ed: 19 Janua y 2021
Accep ed: 9 Feb ua y 2021
Published: 11 Feb ua y 2021
Publishe ’s No e: MDPI s ays neu-
al wi h ega d o ju isdic ional clai-
ms in published maps and ins i u io-
nal a ilia ions.
Copy igh : © 2021 by he au ho s. Li-
censee MDPI, Basel, Swi ze land.
This a icle is an open access a icle
dis ibu ed unde he e ms and con-
di 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/).
1Ha e Depa men o Ma ine Technologies, Cha ney School o Ma ine Sciences, Uni e si y o Hai a,
Hai a 3498838, Is ael; eibi z@uni .hai a.ac.il
2
Depa men o Ma ine Biology, Cha ney School o Ma ine Sciences, Uni e si y o Hai a,
Hai a 3498838
, Is ael;
d che no @uni .hai a.ac.il
3A agón Ins i u e o Enginee ing Resea ch (I3A), Uni e si y o Za agoza, 50009 Za agoza, Spain;
inigo@uniza .es (I.A.); acm@uniza .es (A.C.M.)
4
ARC Cen e o Excellence o Co al Ree S udies, School o Biological Sciences, The Uni e si y o Queensland,
Douglas, QLD 4814, Aus alia; [email p o ec ed]
5The Mina & E e a d Goodman Facul y o Li e Sciences, Ba -Ilan Uni e si y, Rama Gan 5290002, Is ael
6School o Zoology, Tel-A i Uni e si y, Tel A i 6997801, Is ael; [email p o ec ed]
*Co espondence: [email p o ec ed]
† Cu en add ess: Ha e Depa men o Ma ine Technologies & Mo is Kahn Ma ine Resea ch S a ion,
Cha ney School o Ma ine Sciences, Uni e si y o Hai a, Hai a 3498838, Is ael.
Abs ac :
In an endea o o s udy na u al sys ems a mul iple spa ial and axonomic esolu ions,
he e is an u gen need o au oma ed, high- h oughpu amewo ks ha can handle ple ho a o
in o ma ion. The coalescence o emo e-sensing, compu e - ision, and deep-lea ning elici s a new e a
in ecological esea ch. Howe e , in complex sys ems, such as ma ine-ben hic habi a s, key ecological
p ocesses s ill emain enigma ic due o he lack o c oss-scale au oma ed app oaches (mms o kms) o
communi y s uc u e analysis. We add ess his gap by wo king owa ds scalable and comp ehensi e
pho og amme ic su eys, ackling he p o ound challenges o ull seman ic segmen a ion and 3D
g id de ini ion. Full seman ic segmen a ion (whe e e e y pixel is classi ied) is ex emely labou -
in ensi e and di icul o achie e using manual labeling. We p opose using label-augmen a ion, i.e.,
p opaga ion o spa se manual labels, o accele a e he ask o ull segmen a ion o pho omosaics.
Pho omosaics a e syn he ic images gene a ed om a p ojec ed poin -o - iew o a 3D model. In
he lack o na iga ion senso s (e.g., a di e -held came a), i is di icul o epea ably de e mine
he slope-angle o a 3D map. We show his is especially impo an in complex opog aphical
se ings, p e alen in co al- ee s. Speci ically, we e alua e ou app oach on ben hic habi a s, in h ee
di e en en i onmen s in he challenging unde wa e domain. Ou app oach o label-augmen a ion
shows human-le el accu acy in ull segmen a ion o pho omosaics using labeling as spa se as 0.1%,
e alua ed on se e al ecological measu es. Mo eo e , we ound ha g id de ini ion using a le ele
imp o es he consis ency in communi y-me ics ob ained due o occlusions and opology (angle
and dis ance be ween objec s), and ha we we e able o s anda dise he 3D ans o ma ion wi h
wo pe cen e o in size measu emen s. By signi ican ly easing he anno a ion p ocess o ull
segmen a ion and s anda dizing he 3D g id de ini ion we p esen a seman ic mapping me hodology
enabling change-de ec ion, which is p ac ical, swi , and cos -e ec i e. Ou wo k low enables
epea able su eys wi hou pe manen ma ke s and specialized mapping gea , use ul o esea ch
and moni o ing, and ou code is a ailable online. Addi ionally, we elease he Ben hos da a-se , ully
manually labeled pho omosaics om h ee oceanic en i onmen s wi h o e 4500 segmen ed objec s
use ul o esea ch in compu e - ision and ma ine ecology.
Keywo ds:
pho og amme y; o ho ec i ica ion; change-de ec ion; communi y ecology;
label-augmen a ion; co al- ee s; ben hic mapping; compu e - ision; mul i-le el supe pixels
Remo e Sens. 2021,13, 659. h ps://doi.o g/10.3390/ s13040659 h ps://www.mdpi.com/jou nal/ emo esensing
Remo e Sens. 2021,13, 659 2 o 19
1. In oduc ion
Accele a ions in echnologies [
1
] ha e empowe ed ecological s udies by acili a ing
digi al ep esen a ions o na u al sys ems [
2
], hus educing unce ain ies in p edic ing hei
u u e-s a e [
3
]. Ad ances in compu e - ision and emo e-sensing enable c oss-scale e-
sea ch. In he nea u u e, deep neu al ne wo ks will help o deciphe p ocess- om-pa e n
as pa o au oma ed wo k lows; p eceded by da a acquisi ion om obo ic pla o ms and
seman ic segmen a ion o image-based maps [
4
,
5
]. Image-based mapping and seman ic
segmen a ion a e used in an a ay o ecological s udies and applica ions, anging om
s udying ege a ion pa e ns [
6
–
8
] and ci y-scapes [
9
] o a m-managemen [
10
]. Speci -
ically, pho og amme y has become a popula app oach o ben hic esea ch and ee
moni o ing [
11
–
21
]. S uc u e-F om-Mo ion (SFM) pho og amme y es ima es he 3D scene
s uc u e and ela i e mo ion using subsequen images. I is now possible o iew an
ecosys em wi hin a digi al amewo k as a con inuum ac oss spa ial scales, and examine
he indi iduals, popula ions, and communi ies ha comp ise i . Ne e heless, pho og am-
me y is no ye ully ma u e as a epea able me hod o wide scale ecological su eys. Fi s ,
he ou pu 3D models and pho omosaics need o be labeled igo ously o analysis. This is
labo ious and equi es expe knowledge. Thus, he e is an u gen need o au oma ion
in he ull segmen a ion ask (i.e., labeling each pixel) o pho omosaics. Second, a 3D g id
needs o be consis en ly de ined o epea ed su eys. Wi hou p ope da a ex ac ion ha
includes ull, pixel-wise classi ica ion and labeling, he ele an in o ma ion emains con-
cealed in he image. He e, we add ess bo h issues, p o iding a mo e cohe en solu ion o
habi a -mapping and unde wa e pho og amme y. While ou me hods a e applicable o
all domains in which pho og amme y is used, he e we ocus on he ben hic en i onmen .
The e a e inc easing e o s o au oma ic labeling using machine lea ning [
4
,
6
,
9
,
20
,
22
].
Howe e , he commonly used ools [
23
,
24
] s ill p o ide poin classi ica ion and no ull
segmen a ion. Such spa se sampling is o e looking objec /pa ch le el in o ma ion, such
as he mo pho-me ics (shape and size) o indi idual o ganisms ha can be p o ided
by ull seman ic segmen a ion. Se e al me hods o segmen a ion o ben hic images and
pho omosaics ha e been demons a ed [
25
–
29
], including using mul i- iew images [
30
]
and 3D models [
31
]. These wo ks ha a e based on deep lea ning p o ide imp essi e
esul s; howe e , deep neu al ne wo ks ely on a high numbe o lea ning pa ame e s and
because o ha , hey need o be ained wi h a la ge amoun o da a o a oid o e i ing.
Then, he main p oblem o success ul au oma ic iden i ica ion o ma ine species is he lack
o aining da a and ex ensi e a iabili y wi hin axa [
32
,
33
] ha p e en s using labeled
da a om o he loca ions and p edic ing labels ha we e no used in he aining da a. To
o e come his, we p opose p opaga ing spa se labels using ou Mul i-Le el Supe pixel
(MLS) app oach [
25
]. In [
25
] his me hod was sugges ed as a way o quickly gene a e
aining da a o deep lea ning seman ic segmen a ion in se e al e es ial and unde wa e
domains. He e we show ha e en by i sel i enables ob aining as ull segmen a ion
wi h minimal human in e en ion. We es i ex ensi ely on pho omosaics wi h espec o
ecological measu emen s and show ha i p o ides e y high accu acy. Thus, i can be used
as a complimen a y me hod o gene a ing dense aining da a in cases whe e he e a e no
a ailable ained deep ne wo ks as i is gene al and no domain speci ic. Challenges o
deep-lea ning algo i hms in unde wa e imaging include illumina ion and ange, as well
as image deg ada ion caused by e ac ion and wa eleng h-speci ic a enua ion [
34
,
35
].
An o hopho o is gene a ed om a single angle-o - iew on he 3D model h ough he
p ocess o o ho ec i ica ion whe e a planime ically co ec image is c ea ed by emo ing
he e ec s o pe spec i e ( il ) and elie ( e ain). In an o hopho o, he objec s a e scaled
and loca ed in hei ue posi ions ( opology), enabling di ec measu emen s o a eas and
dis ances [
36
]. Howe e , in ansi ion om 3D o 2D (o ho ec i ica ion) he e a e six
deg ees-o - eedom ha need o be se . In opog aphically complex s uc u es, such as
co al ee s, expo ing di e en pe spec i es o he same 3D model a ec s he occlusions
(Figu e 1) and map- opology, as well as a i ac ing and dis o ion on non-plana objec s
wi h limi ed inpu iews. Thus, he dis ance and angle be ween o ganisms may di e
Remo e Sens. 2021,13, 659 3 o 19
wi hou consis ency in o ho ec i ica ion. This can be de imen al, o example, in s udies
ega ding neighbo - ela ions and size-dis ibu ions.
Figu e 1.
The e ec o o ho ec i ica ion wi h a le ele on co al opology, p e alence and size: Th ee pho omosaic eplica es
we e gene a ed subsequen ly. (
a
) G ound- u h (baseline) pho omosaic. (
b
) Replica e which was o ho ec i ied using he
spi i le ele as a e e ence. (
c
) No le ele (Naï e) was o ho ec i ied wi hou in e en ion (3D ans o ma ion). The numbe s
in yellow (le ) a e close-ups on he columns.
Mos solu ions o de ining he plane o p ojec ion y o de ine he Z-axis acco ding
o dep h in he wa e -column. Usually, pe manen ma ke s such as plas ic ubes o s eel
bol s a e used o his pu pose [
15
], and hei dep h and he dis ance be ween hem need o
be measu ed di ec ly o indi ec ly [
37
]. O he means o sol e his p oblem include owed
buoys moun ed wi h GPS senso s [
38
] in shallow wa e su eys, and posi ioning wi h
acous ic da a [
39
]. Ye , hese solu ions a e imp ac ical o deep and emo e ee habi a s
such as Mesopho ic Co al Ecosys ems (MCEs, 30–150 m dep h) [40].
To ackle his p oblem, we de ine he Z-axis as he dep h axis by placing a spi i le ele
wi hin he su ey plo and using i o ans o m he 3D model.
Ben hic habi a mapping using acous ic and op ic senso s encompassess a ange o oci
and scales, om species dis ibu ion models o communi y mapping and abio ic habi a
mapping [
41
]. Op ical imaging can p o ide much g ea e de ail han acous ic senso s,
which ha e wide scalabili y. Howe e , ben hic habi a s a e di icul o map due o he
complex in e ac ions be ween physical, chemical, biological, and beha io al elemen s
ha comp ise hem [
42
]. He e we p esen a mul i-class communi y mapping scheme o
ben hic su eys.
The sessile communi ies ha o m and inhabi he ee a e linked h ough c oss-scale
p ocesses. Fo ins ance, in scle ac inian co als, g ow h- a es and neighbo in e ac ions
occu a e y small spa ial scales, ye hey ope a e wi hin a much mo e expansi e sys em,
whe e dispe sion is enhanced by p eda ion and ex eme wea he e en s [
43
], and ica iance
is e icula e h ough ocean cu en s [
44
]. Acco dingly, bo h he minu e and he eno mous
scales a e signi ican in cha ac e izing he physical and biological ea u es o ee s uc u es.
The composi ion o axa in space and ime has been he ocus o many s udies in ben hic
ecology. Howe e , ee s a e so in ica e (Figu e 2) ha in he lack o adequa e echnology
Remo e Sens. 2021,13, 659 4 o 19
o communi y-le el in es iga ion, he dynamics o sessile o ganisms emain puzzling.
Thus, undamen al ques ions ega ding key ecological p ocesses in he ee ha e emained
la gely he same o o e i e decades [
45
–
49
], as a simpli ied compa men aliza ion o he
ben hos is o en made o handling complex phenomena.
Figu e 2.
The main challenges in ben hic image segmen a ion a e due o plas ici y, i egula shapes,
and elabo a e 3D s uc u es. (
a
) The ben hic communi y s uc u e in Eila , he Red Sea, is composed
mainly o Scle ac inian co als. (
b
) The ee s in he eas e n Ca ibbean a e shi ing owa ds a sponge
and so -co al domina ed communi y. (
c
) In he eas e n Medi e anean, he ocky ee is empo a ily
domina ed by u algae.
In ecological s udies, he scale o in es iga ion depends on he a e o e en s [
50
,
51
].
Ben hic o ganisms ha e g ow h a es on he scale o mms o cms pe yea [
52
]. The e o e,
ou in es iga ion necessi a es cm scale change-de ec ion abili ies. To assess and alida e
he change-de ec ion abili y o ou wo k low, we conduc a epea ed su ey and show
ha such o ho ec i ica ion enables consis en ly examining he g ow h and decay, spa ial
opology, and p esence/absence coun s o sessile ee o ganisms.
Ou me hodology o au oma ed and epea able seman ic mapping can de ec and
eloca e sessile o ganisms on he cm-scale ac oss hund eds o me es. Such a ool can assis
in cons uc ing a mul i-le el, c oss-scale iew o unde wa e and e es ial ecosys ems,
use ul o esea ch and moni o ing e o s. In his pape , we desc ibe i s applica ion on a
new da a-se ha includes manually segmen ed pho omosaics om h ee di e en egions:
a ocky ee in he Eas e n Medi e anean, a co al ee in he No he n Red-Sea, and a co al
communi y in he Eas e n Ca ibbean. We alida e ou app oach h ough compu e - ision
me ics as well as ele an ecological me ics.
Ou speci ic con ibu ions a e:
•
Ex ensi e ecological alida ion o seman ic segmen a ion h ough label-augmen a ion
o spa se anno a ions.
• Valida ion o 3D g id s anda disa ion wi h a consume -g ade spi i -le ele .
•
The Ben hos da a-se ha includes h ee segmen ed pho omosaics om di e en
oceanic en i onmen s.
2. Ma e ials and Me hods
2.1. Imaging Sys em and Pho og amme ic Equipmen
A NIKON D850 came a wi h a 35 mm NIKKOR lens in a Nau icam housing wi h
ou INON Z-240 s obes was used (Figu e 3b). Pho og amme ic a ge s a e objec s wi h
dis inguishable ea u es and o ien a ion. Ou a ge s included measu ing apes, 0.5 m
scale-ba s, unde wa e colou cha s (DGK), a spi i le ele , and di e sla es wi h elec ical
ape ma kings (Figu e 3a).
Remo e Sens. 2021,13, 659 5 o 19
Figu e 3.
Wo k low o seman ic mapping: (
a
) Scale ba s a e loca ed nex o a dis inguishable objec
a he su ey s a ing poin , sla e and colou -ca d a e used as pho og amme ic a ge s, and he
spi i le ele is aligned in he scene and used o 3D g id de ini ion in pos p ocessing. (
b
) Image
acquisi ion is ca ied ou using a di e -held imaging sys em. (
c
) An RGB pho omosaic is p oduced
and (
d
) labeled spa sely. (
e
) Labels a e augmen ed o ull e ain depic ion using Mul i Le el
Supe pixels (MLS). (
) Communi y s a is ics such as class speci ic size- equency dis ibu ion a e
ex ac ed au oma ically.
2.2. Plo Se up and Acquisi ion P o ocol
When eaching he a ge dep h, a dis inguishable na u al o a i icial objec which is
ela i ely simple o na iga e o was de ec ed as a s a ing poin o he su ey. F om ha
poin , we measu ed he equi ed ansec leng h (5–30 m) using a measu ing ape and
ma ked i s su oundings using pho og amme ic a ge s and scale ba s. In he o ho ec i-
ica ion expe imen s, we aligned a spi i le ele in he su ey plo . The spi i le ele has
h ee bubble indica o s (Figu e 3a). When i is placed in such a way ha he bubbles a e
cen ed, he le ele can be used o de ine a plane-o -p ojec ion. Op imally, he le ele was
placed in he cen e o he plo , and pa allel o he ansec . The le ele is used o ans o m
he 3D model, hus i is pa amoun o ob ain a good econs uc ion o i by acqui ing many
(>15) images om di e en angles and dis ances.
Be o e each su ey, se e al es images we e aken o adjus came a se ings: ISO, ape -
u e, shu e speed, and ocus. When eaching he op imal came a se ings he su ey was
ini ia ed, and se ings we e no changed h oughou i . Images we e acqui ed a 1 Hz using
he came a’s in e al ime shoo ing unc ion. The came a was held mainly downwa d-
looking while he di e swam in a lawn-mowe (bous ophodonic) pa e n, pe o ming
close ecip ocal passes o e he su ey plo o ensu e o e lap be ween pa allel legs.

Remo e Sens. 2021,13, 659 6 o 19
2.3. S udy Si es and Da a-Se s
We used image-se s om h ee dis inc oceanic en i onmen s (Figu es 2and 4).
This comes o show he implemen a ion o ou wo k low in di e en ecological zones,
and demons a e he gene ali y o his me hod (Table 1).
Figu e 4.
[Top] The global dis ibu ion o he h ee s udy zones, and he main pho omosaics used in his s udy; he ben hos
da a-se [bo om], (Table 1). (
A
)Spa an Ree o sho e Hai a on he eas e n Medi e anean coas line (
MD
da a-se ). (
B
) IUI o
Eila ee , Gul o Aqaba, no he n Red-Sea (
RS
and
RS20
da a-se s). (
C
)Double-W eck ee , island o S . Eus a ius in he
eas e n Ca ibbean (CR da a-se ).
Table 1.
The di e en da a-se s used in his s udy a e om h ee oceanic egions. Some o he da a-se s a e labeled coa sely
(no all pixels ha e a label) and some a e manually segmen ed ( ull manual labeling; e e y pixel has a label). Classi ica ion
is di ided be ween a genus-speci ic scheme and a lowe le el habi a -mapping scheme (Te ain) wi h eigh classess ha
ep esen he e ain ype.
Region Name Dep h (m) Size in m2Labeling Classi ica ion Map Replica es
Red Sea RS20 20 10 ×1 Coa se Genus 3
Red Sea RS 24–28 5 ×5 Full Te ain 2
Medi e anean MD 20 5 ×4 Full Te ain 2
Ca ibbean CR 20 12 ×2 Full Te ain 1
Remo e Sens. 2021,13, 659 7 o 19
Labeling and Classi ica ion
We used wo manual labeling schemes: coa se labeling (a polygon inside he objec
co e ing i s cen e bu no all o i s pixels) and ull segmen a ion, and wo classi ica ion
schemes: genus-speci ic (57 classes), and habi a mapping (eigh classes) (Table 1). We
used labelbox, a dedica ed ool o compu e - ision applica ions, because o i s lexibili y,
academic p icing bene i s, and simple in e ace. Images we e uploaded and labeled wi h
a polygon p ojec se up. In da a-se Red Sea 20 (
RS20
) we used genus-speci ic classes o
scle ac inian co als, and o he sessile g oups a lowe axonomic esolu ions. In da a-se s
Red-Sea (
RS
), Ca ibbean (
CR
), and Medi e anean (
MD
) we used eigh classes in ull
manual labeling, by he e ain ype. This equi es less expe ise and can be dis ibu ed
among non-expe labele s such as unde -g adua e o high-school s uden s, and e en
ex e nal wo k o ces.
2.4. Label-Augmen a ion
This expe imen e lec s he amoun o labeling e o equi ed in o de o ob ain he
highes quali y o label-augmen a ion.
Augmen a ion om Spa se Anno a ions
Label-augmen a ion consis s o expanding spa se labels o ull segmen a ion by aug-
men ing he numbe o labeled samples. We use he me hod p e iously de eloped by
us [
53
] ha was since alida ed ex ensi ely on di e en ypes o da a including ci y-scape
images o au onomous d i ing, e es ial o hopho os, and luo escen and RGB co al
images [
25
,
54
] (code a ailable online h ps://gi hub.com/Sha he/ML-Supe pixels (accessed
on 19 Janua y 2021)). He e, we examine his me hod wi h espec o meaning ul ecological
measu es. We apply label-augmen a ion on pho omosaics (Figu e 5), whe e he inpu is
spa se anno a ions, and he ou pu is a ully segmen ed map. A supe pixel is a low-le el
g ouping o neighbo ing pixels. The MLS app oach uses supe pixels o p opaga e he
spa se labels. I compu es se e al supe pixel le els o di e en sizes and uses he spa se
anno a ions as o es. I consis s o applying he supe pixel image segmen a ion i e a i ely,
p og essi ely dec easing he numbe o supe pixels gene a ed in each i e a ion. In he i s
i e a ion, he numbe o supe pixels is e y high, leading o e y small-sized supe pixels
o cap u ing small de ails o he images. The ollowing i e a ions dec ease he numbe o
supe pixels, leading o la ge supe pixels co e ing unlabeled pixels. Successi e i e a ions
do no o e w i e in o ma ion; hey only add new labeling in o ma ion un il all pixels
a e co e ed.
Figu e 5.
Augmen a ion alida ion wo k low. (
a
) A 5
×
5 m
2
pho omosaic om he
RS
da a-se .
(
b
) The mosaic was ully labeled manually acco ding o he eigh classes in he colou code ( igh ).
(
c
) The ull labels we e spa si ied ( he example depic s he emaining 0.1% pixels and a magni ica ion
o he op le co ne ). (
d
) The spa se labels we e augmen ed using ou me hod, and (
e
) e alua ed
agains he ull manual labels.
To e alua e he me hod, we conduc ed an expe imen o es ima e how many ini ial
seeds a e equi ed o achie e an accu a e ull segmen a ion and how di e en spa si ies
a ec he augmen a ion pe o mance. As ou pho omosaics we e manually labeled densely,
i.e., all he pixels we e labeled, we simula e he spa se labeling by andomly sampling
Remo e Sens. 2021,13, 659 8 o 19
ini ial seeds in se e al spa si y le els (10%, 1%, 0.1%, 0.01%, 0.001%) o he o iginal dense
labels, and augmen ing i using he same me hod. These spa se labels simula e he way
ben hic da a-se s a e usually labeled o educing he labeling cos .
2.5. O ho ec i ica ion
The pu pose o his expe imen was o simula e epea ed su eys wi hou pe manen
ma ke s o na iga ion senso s. In his manne , epea ed su eys can ake place wi h he
aid o na u al and a i icial e e ences such as dis inc i e ee ea u es o moo ing sinke s.
These objec s se e as a s a ing poin o he su ey, and o hopho os can be egis e ed in
pos -p ocessing as long as hey a e consis en ly o ho ec i ied.
2.5.1. 3D G id De ini ion and O ho ec i ica ion
We used Agiso Me ashape 1.5 o cons uc ing he 3D map models and o hopho-
os (Agiso Me ashape P o essional Ve sion 1.5, Agiso LLC, S . Pe e sbu g, Russia,
2016). In da a-se s
RS20, RS
, and
MD
, a 0.5
×
0.05 m
2
spi i le ele was used o de-
ine he 3D g id. The models we e scaled using he known size o he scale ba s. We
ma ked he poin s o known dis ance on 5–10 images un il he scale e o was lowe
han 0.0005 m. Expo ing he o hopho o has se e al deg ees-o - eedom ha ha e o
be se o epea abili y. The loca ions o h ee co ne s o he spi i le ele we e ma ked
as
(X,Y,Z) = (0, 0, Z),(0, 0.05 m, Z),(0.5 m, 0, Z)
whe e Z is he known dep h measu ed
in si u. This was done wi hin he e e ence pane o Agiso , ma king 15–20 images om
di e en angles and dis ances. The model was hen o a ed and ansla ed acco dingly,
and a pho omosaic was expo ed. O ho ec i ied pho omosaics we e expo ed as .png
image iles a a esolu ion o 0.5 mm pe pixel. These we e hen c opped o he a ea o
in e es and adjus ed o con as in Ma lab using he imadjus unc ion [MATLAB R2019].
2.5.2. Repea ed-Su ey Simula ion
To es ima e he abili y o ou pipeline o o ho ec i ying using a le ele and i s change-
de ec ion sensi i i y we epea ed image acquisi ion wo o h ee imes du ing he same
di e, esul ing in image se s ha cons i u e echnical eplica es. Be ween epea s, he spi i
le ele was mo ed a ound he scene. The g ound- u h pho omosaic ep esen s a i s
empo al epea o baseline su ey, and i was ully manually labeled. The labels we e
hen spa si ied (subsampled), and augmen ed on all eplica es esul ing in ully segmen ed
pho omosaic eplica es. These we e compa ed o he g ound- u h mosaic o e alua ion
(Figu e 6e).
In his expe imen ou eplica es a e expec ed o be iden ical and he nega i e-con ol
(naï e) is expec ed o show he highes a iance om he g ound- u h. To gene a e he
naï e (
no le ele
) pho omosaic, one o he image-se s was expo ed wice, be o e and a e
ans o ma ion. We egis e ed he eplica e o hopho os using Ma lab’s manual image
egis a ion ool cpselec and 15–20 egis a ion poin s (Figu e 6c).
2.6. E alua ion Me ics
In all augmen a ion expe imen s, he augmen ed labels we e e alua ed agains he
o iginal manual dense anno a ions. Se e al me ics we e used o assess he pe o mance o
he augmen a ion including ecall, accu acy (pe pixel) and he In e sec ion o e Union
(IoU, pe class):
Recall =T ue Posi i es
T ue Posi i es +False Nega i es (1)
Accu acy =T ue Posi i es +T ue Nega i es
T ue Posi i es +T ue Nega i es +False Posi i es +False Nega i es (2)
IoU =T ue Posi i es
T ue Posi i es +False Posi i es +False Nega i es (3)
Remo e Sens. 2021,13, 659 9 o 19
Figu e 6.
Tes ing o ho ec i ica ion h ough label-augmen a ion. Two pho omosaics a e gene a ed
subsequen ly, he g ound- u h ( op) ep esen s he baseline su ey, and he eplica e (bo om)
ep esen s he empo al epea . (
a
) The g ound- u h (baseline) pho omosaic is labeled. (
b
) Labels
a e spa si ied (
c
) Manual egis a ion o pho omosaics is done using dis inc i e ea u es in he
scene. (
d
) Spa se labels om (
b
) a e augmen ed on he baseline and ans o med mosaic eplica e.
(e) augmen ed maps a e used o e alua ion.
These me ics a e no mally used o assess he pe o mance o CNNs in segmen a-
ion asks.
2.7. Communi y-Me ics Compa isons
We de eloped a Ma lab code o communi y da a ex ac ion. All he objec s below size
0.0002 m
2
we e excluded om analysis because hey come om noise in he segmen a ions.
•Class-speci ic size- equency dis ibu ions.
We di ided he classes in nine bins,
s a ing om 0.0002 m
2
o 0.045 m
2
wi h a s ep size o 0.005 m
2
. We used
χ2
dis ance
o assess he simila i y o class size dis ibu ion be ween maps. Low alues indica e
high simila i y be ween se s o da a whe e ze o is he maximal simila i y.
χ2Dis ance =
n
∑
i=1
(Obse edi−Expec edi)2
Obse edi+Expec edi
(4)
•Rela i e amoun o indi iduals pe class.
The numbe o objec s om each class
di ided by he o al numbe o objec s in he map.
•Rela i e a ea by class.
The size in m
2
pe class di ided by he o al size o he map.
The pho omosaics a e expo ed a 0.5 mm pe pixel, and o ans e o m
2
we use he
ollowing equa ion:
Size in m2=∑Pixels
4×10−6(5)
3. Resul s
3.1. Label-Augmen a ion
In his expe imen we used ully manually labeled images o es he MLS augmen-
a ion app oach om spa se seeds on wide scale da a; pho omosaics om di e en ee
en i onmen s. We used da a-se s
RS, MD
, and
CR
. The label-augmen a ion expe imen
shows ha augmen ed labeling and dense manual anno a ions p o ide e y simila ecolog-
ical ou pu s. Figu e 7depic s bo h he pe -pixel accu acy and he IoU o all spa si y le els.
The pe -pixel me ic (accu acy) is highe because o he backg ound classes (Sand, Rock)
Remo e Sens. 2021,13, 659 16 o 19
Howe e , compa ing he simila i y o o hopho os is no s aigh o wa d, due o di e ences
such as colo and a i ac s (blu /holes) caused o example by sligh di e ences in he
dis ance and angle o image. We compa ed he maps indi ec ly h ough label-augmen a ion.
Compa ing he segmen ed maps gene a ed om augmen ing a single se o spa se labels
( om he o iginal image) es s all s eps o he wo k low in ac , and includes noise om
he pho og amme ic (di e en inpu images) and o ho ec i ica ion p ocesses. Thus, i
simula es an obse e e ec and a noisy eal-wo ld si ua ion.
When applying his wo k low in any se ing, he mos impo an ac o s o conside
a e he classi ica ion le el ( axonomic/ unc ional speci ici y), as i implies on he le el o
expe knowledge equi ed as well as he accu acy in au oma ic iden i ica ion, and he
expec ed change-de ec ion abili y which is go e ned by he e ec i e esolu ion and signal-
o-noise a io. Fu he mo e, i is impo an o conside he e ec o he slope on he ee ,
in he sense ha he op down iew is no always pe pendicula o he ee - able.
A he momen , he e a e se e al ools o image segmen a ion wi h weak human-
in e e ence [
67
]. Mo eo e , new ools will soon be eleased wi h p omising ou look on he
ben hic pho omosaic segmen a ion asks [68].
Au ho Con ibu ions:
Concep ualiza ion, All Au ho s; me hodology, M.Y., T.T., I.A., and A.C.M.
alida ion, M.Y. and I.A.; o mal analysis, M.Y., I.A., T.T., and A.C.M.; in es iga ion, M.Y., I.A.;
esou ces, M.Y., T.T., I.A., and A.C.M.; da a cu a ion, M.Y., T.T.; w i ing—o iginal d a p epa a ion,
M.Y., I.A., T.T.; w i ing— e iew and edi ing, All au ho s; isualiza ion, M.Y., I.A.; supe ision, T.T.,
D.T., A.C.M.; p ojec adminis a ion; M.Y.; unding acquisi ion, M.Y., T.T. All au ho s ha e ead and
ag eed o he published e sion o he manusc ip .
Funding:
T.T. was suppo ed by he The Leona M. and Ha y B. Helmsley Cha i able T us , The
Mau ice Ha e Founda ion, he Is ael Minis y o Na ional In as uc u es, Ene gy and Wa e
Resou ces G an 218-17-008, he Is ael Minis y o Science, Technology and Space g an 3-12487,
and he Technion Ollendo Mine a Cen e o Vision and Image Sciences. I.A. and A.C.M. we e
suppo ed by p ojec PGC2018-098817-A-I00 MCIU/AEI/FEDER, UE. M.Y. was suppo ed by he
PADI Founda ion (applica ion #32618), he Mu ay Founda ion o s uden esea ch, ASSEMBLE+
Eu opean Ho izon 2020 ( ansna ional access #216), and Mic oso AI o Ea h; AI o Co al Ree
Mapping. Y.L. was unded by he Is ael Science Founda ion (ISF) g an No. 1191/16. GE was
suppo ed by he Eu opean Union’s Ho izon 2020 esea ch and inno a ion p og am unde he Ma ie
Skłodowska-Cu ie g an ag eemen #796025.
Da a A ailabili y S a emen :
The Ben hos da a-se and Ma lab code is a ailable in he D yad Digi al
Reposi o y: h ps://doi.o g/10.5061/d yad.8cz8w9gm3 The code o ML Supe pixels can be ound
a : h ps://gi hub.com/Sha he/ML-Supe pixels.
Acknowledgmen s:
We hank he Mo is-Kahn Ma ine Resea ch S a ion, he In e uni e si y Ins i u e
o Ma ine Sciences o Eila , and he Ca ibbean Ne he land Science Ins i u e o making hei acili ies
a ailable o us, and mos impo an ly he s uden s, s a , and di ing eams o hese acili ies o
ieldwo k and echnical assis ance; A iad A ni, Debo ah Le i, Assa Le i, Ophe Ba -Na han, Leonid
Deh e , Yu al Gold ach , Sha on Fa be , Ilan Ma dix, Inbal Ayalon, Li az Le y, Lindsay Boni o, Pim
Bongae s, Basha Elnasha , De ya Akkaynak, and A i Ba -Massada o aluable in ellec ual and
echnical con ibu ions; The image labeling eam: Shai Zilbe man, Gal E ia a , Adi Zwei le , Osh a
Yosse , Ma Dohe y; Guilhem Banc-P andi o he pic u e in Figu e 3b; Ne a Kashe o d awing
he g aphical abs ac ; NVIDIA Co po a ion o he dona ion o he Ti an Xp GPU used in his wo k.
Fieldwo k in Eila was ca ied ou unde pe mi #42-128 om he Is aeli Na u e and Pa ks Au ho i y.
Con lic s o In e es : The au ho s decla e no con lic o in e es .
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