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A new model to analyze the temperature effect on the microalgae performance at large scale raceway reactors

Abstract

In this paper a simplified temperature model for raceway reactors is developed, allowing to determine the temperature of the microalgae culture as a function of reactor design and environmental conditions. The model considers the major phenomena taking place in raceway reactors, especially heat absorption by radiation and heat losses by evaporation among others. The characteristic parameters of the model have been calibrated using genetic algorithms, next being validated with a long set of more than 50 days covering different weather conditions. It is worth to highlight the use of the developed model as a tool to analyze the influence of the temperature on the performance of microalgae cultures at large scale. As example, the annual variation of the performance of up to five different microalgae strains has been determined by computing the temperature index, thus the normalized value of performance of whatever microalgae at the real temperature with respect to that achievable at optimal temperature can be established. Results confirm that only strains tolerant to wide ranges of temperature can be efficiently produced all the year around in large scale outdoor raceway reactors without additional temperature control systems.

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A new model to analyze the temperature effect on the microalgae performance at large scale raceway reactors

Author: Rodríguez-Miranda, E.,Acién Fernández, Francisco Gabriel,Guzmán Sánchez, José Luis,Berenguel Soria, Manuel,Visioli, A.
Publisher: Universidad de Almería
Year: 2020
Source: https://repositorio.ual.es/bitstream/10835/13321/1/2020%20A%20new%20model%20to%20analyze%20the%20temperature%20effect%20on%20the%20microalgae%20performance%20at%20large%20scale%20raceway%20reactors..pdf
A new model o analyze he empe a u e
e ec on he mic oalgae pe o mance a la ge
scale aceway eac o s
E. Rod íguez-Mi anda,†F.G. Acién,‡J.L. Guzmán,∗,¶M. Be enguel,,¶and A.
Visioli,†
†Depa men o Mechanical and Indus ial Enginee ing, Uni e si y o B escia, 25123, I aly
‡Dep. de Ingenie ía, Uni e sidad de Alme ía, CIESOL, 04120 Alme ía, Spain
¶Dep. de In o má ica, Uni e sidad de Alme ía, CIESOL ceiA3, 04120 Alme ía, Spain
E-mail: [email p o ec ed]
1
Abs ac
In his pape a simpli ied empe a u e model o aceway eac o s is de eloped, allowing
o de e mine he empe a u e o he mic oalgae cul u e as a unc ion o eac o design and
en i onmen al condi ions. The model conside s he majo phenomena aking place in aceway
eac o s, especially hea abso p ion by adia ion and hea losses by e apo a ion among o he s.
The cha ac e is ic pa ame e s o he model ha e been calib a ed using gene ic algo i hms, nex
being alida ed wi h a long se o mo e han 50 days co e ing di e en wea he condi ions. I
is wo h o highligh he use o he de eloped model as a ool o analyze he in luence o he
empe a u e on he pe o mance o mic oalgae cul u es a la ge scale. As example, he annual
a ia ion o he pe o mance o up o i e di e en mic oalgae s ains has been de e mined
by compu ing he empe a u e index, hus he no malized alue o pe o mance o wha e e
mic oalgae a he eal empe a u e wi h espec o ha achie able a op imal empe a u e can
be es ablished. Resul s con i m ha only s ains ole an o wide anges o empe a u e can
be e icien ly p oduced all he yea a ound in la ge scale ou doo aceway eac o s wi hou
addi ional empe a u e con ol sys ems.
Keywo ds: Bio echnology, Mic oalgae, Tempe a u e model, Raceway eac o , Ene gy Bal-
ance.
2
In oduc ion
Nowadays, he implemen a ion o mic oalgae eac o s o biomass p oduc ion is expanding due
o he ad an ages and p oduc s ha can be ob ained om hei exploi a ion. F om mic oalgae
biomass, high- alue p oduc s can be ob ained o be used in he chemical indus y1o o ani-
mal ood p oduc ion, such as ish- ood.2Ano he in e es ing ype o applica ion o mic oalgae
biomass, which is cu en ly unde in es iga ion, is he bio uel p oduc ion.3–6 On he o he hand,
he use o was ewa e as a cul u e medium is allowing he de elopmen o new combined applica-
ions such as he simul aneous ea men and pu i ica ion o wa e plus he p oduc ion o biomass
in a single p ocess.7This solu ion is becoming popula because i allows educing ope a ing cos s
and enhancing he use o mic oalgae o low alue applica ions, such as bio e ilize s o bioene gy.
The de elopmen o his ype o applica ions is ca ied ou in aceway eac o s, which a e he mos
ex ended ype o eac o s because hey a e less expensi e and easy o ope a e han ubula -closed
pho obio eac o s.
In addi ion o nu ien supply, he mos ele an a iables in luencing he mic oalgae p oduc ion
p ocesses a e empe a u e, sola adia ion, pH, and dissol ed oxygen.8,9 Tempe a u e and sola
adia ion a e mainly a unc ion o he loca ion whe e he eac o is ins alled and he season o
he yea . The a iables o be con olled a e pH and dissol ed oxygen, in o de o main ain hem
a speci ic ope a ing le els despi e changes in dis u bances, such as sola adia ion.10 Fo ha
eason, de ailed models o he pH and dissol ed oxygen e olu ion in aceway pho obio eac o s
can be ound in li e a u e.11,12 No ice ha he cul u e empe a u e could also be con olled by
using solu ions based on hea exchange s o ex e nal boile s, bu his op ion is omi ed because
i inc eases on he ope a ion cos s. Howe e , i is impo an o ha e dynamical models o he
cul u e empe a u e e olu ion in pho obio ec o s ha can be used as eac o design ools o o
s ain selec ion based on he eac o loca ion.
Biological mic oalgae models can help o es ima e and maximize c op p oduc i i y,13 as well
as cha ac e is ic pa ame e s ha can be used in con ol sys ems o maximize biomass p oduc-
ion.8,10,14 Howe e , al hough he e exis some s udies combining he mic oalgae p oduc i i y and
3
cul u e empe a u e,15,16 mos exis ing biological models do no ake he cul u e empe a u e in o
accoun , wha is a limi ing ac o in he analysis o he mic oalgae p oduc i i y esul s.17–20 Béche
e al. p esen ed a uni e sal empe a u e model o open eac o s,21 which makes use o dimension-
less pa ame e s o hea ans e and e apo a ion phenomena. The e apo a ion phenomenon is a
complex p ocess and di icul o es ima e. In22 a compa ison o di e en e apo a ion models is
p esen ed. On he o he hand, in,23 a dynamic model o he cul i a ion o mic oalgae is de el-
oped whe e an empi ical empe a u e model based on he mal ene gy balances sugges ed in24 is
included. These s udies demons a ed he impo ance o empe a u e on mic oalgae g ow h and
he complexi y o accu a ely es ima ing i s alue. The combina ion o a empe a u e model wi h
he cu en mic oalgae g ow h models would allow a g ea e accu acy in he ep esen a ion o he
mic oalgae beha iou . Thanks o his combina ion, be e con ol a chi ec u es o biomass p o-
duc ion and associa ed applica ions could be de eloped.
In his a icle, a new simple empe a u e model is p esen ed, based on a e iew o he empi ical
ela ionships de ined by Béche e al. and Slege s e al. in,21,24 and adap ed o a aceway eac o .
The cul u e empe a u e is calcula ed om a he mal balance in he eac o , aking in o accoun
all a ailable en i onmen al a iables. This model allows he es ima ion o he empe a u e o he
cul u e in he eac o o ce ain en i onmen al condi ions. In his way, he model could es ima e
pa ame e s o in e es , such as he ime o ha es o an icipa e isk empe a u es ha can nega-
i ely a ec he c op. In addi ion, he model may be used o analyse he empe a u e impac on
biomass p oduc ion o di e en loca ions. In his way, design ools could be de eloped o s udy
he iabili y o he mic oalgae p oduc ion zones o de e mine he mos sui able cul i a ion s ains.
Mo eo e , he empe a u e model can be used o imp o e exis ing mic oalgae es ima ion models
o biomass g ow h models, such as hose p esen ed in11 and.25 Also, he empe a u e model can be
used when he e is a lack o empe a u e measu emen s in he eac o , being used as a empe a u e
es ima o .
The a icle is di ided in he ollowing way. Sec ion 2 p esen s he eac o ha was used o
collec he eal da a and o alida e he models. In Sec ion 3, he componen s o he he mal
4
(a) Real aceway eac o . (b) Reac o scheme.
Figu e 1: Raceway eac o and s uc u e scheme.
balance and he empe a u e model a e de ailed. Sec ion 4 p esen s he esul s ob ained using he
empe a u e model, along wi h an analysis o how empe a u e in luences i e mic oalgae s ains by
using he empe a u e model and he g ow h a e model. Finally, Sec ion 5 s a es he conclusions.
Ma e ial and me hods
This sec ion p esen s de ailed in o ma ion abou he eac o , as well as he mic oalgae cul i a ed
s ain and he measu emen s.
Raceway eac o
The mic oalgae aceway eac o used o he es (Figu e 1a) is loca ed a he IFAPA cen e, nex
o he Uni e si y o Alme ía (Alme ía, Spain). The eac o has a o al su ace o 80 m2, composed
o wo 80 mleng h channels connec ed by a 1 mwide U-shaped bends. Mixing is pe o med by
a paddlewheel o aluminum blades wi h a diame e o 1.5 m, d i en by an elec ic mo o (W12
35 kW, 1500 pm, Eba ba, Ba celona, Spain), wi h gea educ ion (WEB Ibé ica S.A., Ba celona,
Spain). The paddlewheel speed is con olled wi h a equency in e e (CFW 08 WEB Ibé ica,
S.A., Ba celona, Spain) a a cons an eloci y o 0.2 m/s. Ca bona ion is pe o med in a sump
loca ed 1.8 mdowns eam o he paddlewheel, which dimensions a e 1.0 mdep h, 0.65 mleng h
and 1.0 mwid h. In his sump, CO2gas o ai can be injec ed h ough h ee pla e memb ane
5

di use s a he bo om o he sump (AFD 270, EcoTec, Spain). The aceway channels a e made o
low densi y polye hylene o 3 mm hickness while he cu es and sump a e made o high densi y
polye hylene o 3 mm hickness.
In he eac o , he e a e i e pH p obes, i e dissol ed oxygen p obes, and 5 empe a u e p obes.
Figu e 1b shows a scheme o he sys em, whe e each ed poin consis s o a senso se ha includes
pH, dissol ed oxygen, and empe a u e p obes. Poin s one, wo and h ee con ain p obes om
C ison, while poin s ou and i e con ain p obes om Hamil on.
The measu emen s o he clima ic condi ions a e ob ained om a me eo ological s a ion, while
he empe a u e o he soil and he dep h o he cul u e a e measu ed wi h senso s inco po a ed in
he aceway eac o i sel . Table 1 shows he model o he senso s o he measu able a iables,
which ep esen he inpu s o he empe a u e model. The sampling pe iod o he measu emen s
is one second.
Table 1: Measu ing senso s
Measu e Model
Wind speed Anemome e Thies Clima 4.3400.30.000
Global sola i adiance Py anome e Kipp & Zonen CM 6B
Ambien empe a u e and humidi y Senso Del a Ohm HD 9008TRR
Cul u e and soil empe a u e T ansduce PT100 wi h signal condi ione
Cul u e dep h Ul asound senso Wenglo UMD402U035
Mic oalgae s ain
The mic oalgae s ain used in he eac o belongs o Scenedesmus alme iensis (CCAP 276/24)
species. A de ailed s udy abou i s cha ac e is ic pa ame e s and condi ions ela ed o pH, dissol ed
oxygen and empe a u e can be ound in.26 The pH alue anges om 3 up o 10, bu he ne
pho osyn hesis a e is close o he maximal alue om 5.7 o 8. Rega ding he empe a u e, he
alue anges om 12 o 46 ◦C, bu he op imum ange is a ound 30 ◦C. The cul u e medium used
in he g ow h o he mic oalgae has been eshwa e and Mann & Mye s medium p epa ed using
e ilize s (0.14 g·L−1K(PO4)2, 0.18 g·L−1Mg(SO4)2, 0.9 g·L−1NaNO3, 0.02 mL ·L−1Welg o,
6
and 0.02 g·L−1Kalen ol).27
The mal balance and empe a u e model
The he mal balance desc ibed in his pape is based on i s p inciples and empi ical equa ions
de ined o he ans e o ene gy due o sola i adiance, long wa e adia ion, e apo a ion, con-
ec ion, and conduc ion.
Based on he models desc ibed in,21,24 he ene gy balances ha a ec he cul u e ha e been
analysed and es ablished, and a new he mal balance has been de eloped o es ima e he cul u e
empe a u e in he eac o om measu able a iables. The sola i adiance inpu comes om da a
measu ed by he global (di ec + di use) adia ion senso men ioned abo e. Long-wa e adia ion
losses a e calcula ed by he S e an-Bol zmann Law (28). The e a e di e en me hodologies in he
li e a u e o ob ain he e apo a ion low21.In his case, he ene gy balance by e apo a ion is calcu-
la ed om he e apo a ion a e ob ained om an expe imen al e apo a ion exchange coe icien .
Con ec ion is exp essed by New on’s Law o cooling, and inally, conduc ion is exp essed as he
hea ans e be ween he mass o he cul u e in he eac o and he polye hylene laye ha insula es
he eac o om he g ound. As a esul o he in oduced ene gy balances, he he mal balance is
exp essed by he ollowing equa ion (Qiin W):
Qaccumula ed =Qi adiance +Q adia ion +Qe apo a ion +Qcon ec ion +Qconduc ion (1)
whe e Qaccumula ed is he hea accumula ed in he eac o , Qi adiance ep esen s he low o hea
om sunligh , Q adia ion is he long-wa e adia ion hea low, Qe apo a ion accoun s o he hea
low p oduced by he e apo a ion p ocess, Qcon ec ion is he hea low caused by con ec ion and
Qconduc ion ep esen s he hea low be ween he eac o and he polye hylene laye unde i h ough
a conduc ion p ocess.
7
Accumula ed hea low
The hea accumula ed in he eac o ep esen s he sum o all ene gy e ms ha a ec he eac o ,
and i is exp essed by he ollowing equa ion:
Qaccumula ed =h·A·Cp·ρ·dTw
d (2)
wi h h(m) he cul u e dep h, A(m2) he su ace o he eac o , Cp(J kg−1◦C−1) he speci ic hea
capaci y o he cul u e, ρ(kg m−3) he densi y o he cul u e and Tw(◦C) he empe a u e o he
cul u e in he eac o .
Hea low due o he e ec o sola i adiance
The hea low due o inciden sola i adiance on he eac o su ace ep esen s he main hea inpu
in o he eac o . I is exp essed by he ollowing equa ion:
Qi adiance =Ig·a·A(3)
whe e Ig(W m−2)is he global (di ec + di use) sola i adiance, a(−)is he abso p i i y, and
A(m2) ep esen s he o al a ea o he eac o .
Radia ion hea losses
The eac o emi s he mal ene gy as long-wa e adia ion. The low o adia ed ene gy be ween he
eac o and he sky is calcula ed using he ollowing equa ion:
Q adia ion =σ·A·e·Tsky4−(Tw+273.15)4(4)
wi h σ(W m−2K−4) he S e an-Bol zmann cons an , e(−) he wa e emissi i y and Tsky (K) he
equi alen empe a u e o he sky, exp essed in (28) wi h he ollowing exp ession:
8
Tsky = (273.15+Tamb)(0.711+0.0056·Tdew ·0.000073·T2
dew +0.13·cos(15· sola ))0.25 (5)
whe e Tamb (◦C)is he ambien empe a u e, Tdew (◦C) he dew poin empe a u e, and sola (−)
ep esen s he numbe o hou s a e midnigh .
E apo a ion hea low
The e apo a ion p ocess ep esen s he main sou ce o hea loss in he eac o and depends on he
shape o he eac o , he e apo a ion a e and he la en hea o apo iza ion, as p esen ed in (29).
The e apo a ion hea low is de e mined as ollows:
Qe apo a ion =A·Ep·ρ·h g (6)
whe e Ep(m s−1)is he e apo a ion a e, ρ(kg m−3)is he densi y o he cul u e and h g (J kg−1)
is he la en hea o apo iza ion, exp essed as ollow:
h g = (2494−2.2·Tw)·1000 (7)
The e apo a ion a e can be calcula ed as an empi ical equa ion which depends on he di e -
ence in apou p essu es be ween he ambien ai and he eac o cul u e mass (29,30), in addi ion
o an e apo a ion exchange coe icien which depends on wind speed Ws:
Ep=RH ·p0
A
100 −p0
A·he ap (8)
whe e RH (%)is he ela i e humidi y, p0
A(Pa)is he apo p essu e o he ai a ambien empe a-
u e and he ap (m s−1Pa−1)is an e apo a ion exchange coe icien , ob ained expe imen ally om
he ollowing equa ion:
9
Figu e 3: Tempe a u e calib a ion esul s. Each indi idual colo plo ep esen s h ee consecu-
i e days o he selec ed mon hs om Augus o Decembe . Dashed lines ep esen eal eac o
empe a u e while solid lines ep esen es ima ed empe a u e. Fo he co ec isualiza ion o he
colo s in he g aphs, e e o he web e sion o he pape .
model and e i y ha i ai h ully ep esen s he dynamics o he sys em, ega dless o he mon h.
Figu e 5 shows he alida ion esul s o he empe a u e model, whe e each mon h is ep esen ed
indi idually ollowing he same han o he calib a ion esul s. The model ollows he dynamics
o he cul u e empe a u e in he eac o , wi h a maximum e o o 3.9 [◦C] and a mean e o o
0.86 [◦C]. Fo he en i e da a se an RMSE alue o 1.03 [◦C] has been ob ained.
As in he calib a ion esul s shown in Figu e 3, he es ima ed empe a u e o he mon hs o
Augus and Sep embe adequa ely esembles he eal empe a u e o he eac o , wi h a mean e o
o 0.5 [◦C]. The esul s o he mon h o Oc obe du ing he day ime pe iod a e e y sa is ac o y,
howe e , du ing he nigh ime he e a e ce ain disc epancies, inc easing he mean e o o 0.95
[◦C]. These e o s, like in he las ep esen ed day o Oc obe , may be due o e o s in he mea-
su emen s o he inpu a iables o isola ed punc ual phenomena ha a ec he empe a u e o he
eac o . On he o he hand, he mon hs o No embe and Decembe ha e a g ea e e o (mean
e o o 1.15 [◦C]) in he es ima ion, al hough he dynamics esembles he eal empe a u e and he
esul s a e sa is ac o y.
16

Figu e 4: En i onmen al inpu a iables o alida ion. Each mon h ( om Augus o Decembe )
is ep esen ed by di e en colo s and i is made up o 10 consecu i e days each. Fo he co ec
isualiza ion o he colo s in he g aphs, e e o he web e sion o he pape .
Figu e 5: Tempe a u e alida ion esul s. E e y indi idual colo plo ep esen s en consecu i e
days o he selec ed mon hs om Augus o Decembe . Solid line ep esen s es ima ed empe -
a u e while dashed line ep esen s eal eac o empe a u e. Fo he co ec isualiza ion o he
colo s in he g aphs, e e o he web e sion o he pape .
17
Tempe a u e in luence on mic oalgae ac i i y o di e en s ains
Using he de eloped empe a u e model, an analysis on how empe a u e in luences on mic oalgae
g ow h was ca ied ou o i e mic oalgae s ains. Fo his issue, he empe a u e-e ec on g ow h
model p esen ed by Be na d e al. in16 was used oge he wi h he empe a u e model desc ibed in
his pape .
The mic oalgae speci ic g ow h a e model has been used ex ensi ely in li e a u e16,26 and was
o mula ed by Camacho-Rubio e al. in.34 This model s a es ha he mic oalgae g ow h a e, µ,
is made up o ou ac o s ha depend on pho osyn he ically ac i e adia ion and ligh a ailabili y
inside he cul u e (Ia ), cul u e empe a u e (Tw), he pH, and he dissol ed oxygen (DO) in he
eac o . The g ow h model is desc ibed by he ollowing equa ion:
µ=µ(Ia )·µ(Tw)·µ(pH)·µ(DO)(17)
The speci ic g ow h a e (µ) is mainly a unc ion o ligh a ailabili y inside he eac o summa-
ized by he a e age i adiance inside he cul u e (Ia ) (35). This unc ion is exp essed as ollows:
µ(Ia ) = µmax ·Ia n
Ikn+Ia n(18)
whe e µmax [day−1]is he maximum g ow h a e, Ia [µE m−2s−1]is he ligh a ailabili y inside he
eac o summa ized by he a e age i adiance inside he cul u e, Ik[µE m−2s−1]is he minimum
ligh needed by he mic oalgae o achie e maximum pho osyn hesis and n[−]is a o m pa ame e .
Fo a speci ic geome y, he a e age i adiance (Ia ) is a unc ion o he ligh pa h inside he
cul u e, he biomass concen a ion and he ex inc ion coe icien o he biomass. The speci ic
g ow h a e hype bolically inc eases wi h he a e age i adiance up o achie e he maximum spe-
ci ic g ow h a e µmax o he selec ed s ain. Wha e e he mic oalgae s ains, o any ope a ional
condi ions a ix speci ic g ow h a e is achie ed, being highe o lowe acco ding o he op imal
alue o o he cul u es pa ame e s such as empe a u e, pH and dissol ed oxygen among o he s.
The ac o s o empe a u e, pH and dissol ed oxygen a e no malized alues and he o e line
18
indica es ha he e m a ies be ween 0 and 1, which mul iply he sola adia ion pa ame e . The e-
o e, when hese h ee (Tw,pH and DO) pa ame e s a e op imal and ha e a alue o 1, he speci ic
g ow h a e only depends on sola adia ion and would ha e he maximum possible alue. How-
e e , i any o hese pa ame e s is no op imal, i would ha e a di ec nega i e impac on he g ow h
a e.
The empe a u e index (µ(Tw)) is a pa ame e ha ep esen s he in luence o empe a u e on
mic oalgae g ow h, di ec ly ela ed o biomass g ow h, whe e 1 means he maximum yield due o
an op imal empe a u e o he cul u e. The biomass g ow h pe o mance can be diminished by he
e ec o he empe a u e, he e o e a empe a u e abo e o below he cha ac e is ic limi s o he
mic oalgae would esul in null g ow h. Fo example, a s ain ha does no exceed a empe a u e
index o 0.5 in a loca ion means ha a mos , i is no capable o eaching hal i s maximum g ow h
a e, so i would be limi ed o a g ea ex en due o empe a u e condi ions. Thus, he empe a u e
index can be used independen ly o analyze he in luence o empe a u e on mic oalgae s ains, as
i has a di ec e ec on he speci ic g ow h a e.
As commen ed abo e, he es o ac o s in equa ion (17) a e no malized ac o s ha a ec s
µ(IPAR). Speci ically, he empe a u e index can be ob ained om he ollowing equa ion, based
on he maximum (Tmax), minimum (Tmin) and op imum (Top ) empe a u e alues o he mic oalgae
s ain, shown in Table 4:
µ(Tw) = (Tw−Tmax)·(Tw−Tmin)2
(Top −Tmin)·((Top −Tmin)·(Tw−Top )−(Top −Tmax)·(Top +Tmin −2·Tw)) (19)
whe e Tw[◦C]is he empe a u e o he cul u e, calcula ed wi h he empe a u e model desc ibed
in equa ion (15).
The analysis has been done wi h ep esen a i e da a o 8 days o each seasonal pe iod o e a
yea a Alme ía, in Spain, cha ac e ized by mode a e empe a u es in summe and empe a e in
win e . The clima e in Alme ía is conside ed a local s eppe clima e, wi h li le ain all. Du ing he
19
cou se o he yea , he empe a u e gene ally a ies om 8 [◦C] o 30 [◦C] and a ely d ops below
6 [◦C] o ises abo e 35 [◦C]. The objec i e has been o e i y he in luence o empe a u e on
mic oalgae cul i a ion o i e di e en species o mic oalgae h oughou an annual pe iod in his
loca ion. These mic oalgae species co espond o Dunaliella e iolec a,Nannochlo opsis ocean-
ica,Chlo ella py enoidosa and Spi ulina pla ensis, being commonly used o biomass p oduc ion
a indus ial scale, in addi ion o Scenedesmus alme iensis, he s ain used in he aceway eac o
s udied. Table 4 ep esen s he cha ac e is ic empe a u e pa ame e s o each mic oalgae s ain,
applied o he empe a u e index model and ob ained om he li e a u e (16,26) and expe imen al
es s in ou esea ch g oup. Despi e he ac ha he mic oalgae used in he eac o is Scenedesmus
alme iensis, he empe a u e model is independen o he ype o s ain used, because i is a model
o es ima e he cul u e empe a u e. The cha ac e is ic empe a u e pa ame e s o each s ain a e
necessa y in he ca dinal model (equa ion 19), which in combina ion wi h he empe a u e model,
allows o analyze i s in luence o any mic oalgae s ain.
Table 4: Mic oalgae cha ac e is ic empe a u es
Mic oalgae s ain Tmin [°C] Top [°C] Tmax [°C]
Scenedesmus alme iensis 12 30 46
Dunaliella e iolec a 5 32.6 38.9
Nannochlo opsis oceanica -0.2 26.7 33
Chlo ella py enoidosa 5.2 38.7 45.8
Spi ulina pla ensis 7.7 37 50.6
Figu e 6 ep esen s he analysis ca ied ou o he i e ypes o mic oalgae du ing 8 days o
each season o he yea . The i s i e g aphs ep esen he empe a u e ac o (16) ha a ec s
he mic oalgae g ow h. The las g aph a he bo om ep esen s he es ima ed empe a u e in he
aceway eac o o he en i e da a se using he empe a u e model. The ideal seasons o cul i a e
he mic oalgae Scenedesmus alme iensis, used in he eac o desc ibed in Sec ion 2, a e he las
hal o sp ing, he summe and he i s hal o au umn. Howe e , du ing win e , he empe a u e
index is p ac ically 0, which deno es ze o g ow h. The Dunaliella e iolec a s ain is esis an o
medium/high empe a u es and wi h a good empe a u e index la e sp ing, summe and ea ly au-
umn, while i s pe o mance can be diminished by he low empe a u es o win e . The mic oalgae
20
Figu e 6: Tempe a u e index analysis du ing seasonal pe iods. The esul s o he da a se o eigh
days a e ep esen ed indi idually and di ided in ou colou s ep esen ing he di e en seasons.
Fi s g aph co esponds o Scenedesmus alme iensis. Second g aph co esponds o Dunaliella
e iolec a. Thi d g aph co esponds o Nannochlo opsis oceanica. Fou h g aph co esponds o
Chlo ella py enoidosa, while i h g aph co esponds o Spi ulina pla ensis. Six h g aph ep esen s
he es ima ed empe a u e in he aceway eac o (dashed line). Fo he co ec isualiza ion o he
colo s in he g aphs, e e o he web e sion o he pape .
Nannochlo opsis oceanica would no esis he summe pe iod bu i shows good esul s du ing
he es o he yea , especially in win e , whe e i s p oduc i i y exceeds he o he s ains analyzed.
Bo h Chlo ella py enoidosa and Spi ulina pla ensis s ains show a good empe a u e index du ing
he summe pe iod, oge he wi h la e sp ing and he ea ly au umn, as o Dunaliella e iolec a,
in con as o p ac ically no g ow h in win e due o low empe a u es. The esul s ob ained show
a clea ela ionship wi h he cha ac e is ic alues o each s ain ep esen ed in Table 4 allowing an
es ima ion o he iabili y o each s ain o he s udied loca ion.
Discussion
The e o ob ained in Figu es 3 and 5 deno es a p omising accu acy in he model ob ained om
he mal balances. F om he biological poin o iew, he e o ela ed o he es ima ed and he ac ual
empe a u e would no be a p oblem acco ding o he global p ocess dynamics. The model is able
21

o accu a ely ep esen he empe a u e du ing he whole day. Howe e , no ice ha in some days
he e o is la ge han in o he s. These misma ches may be due o he exis ence o non-measu able
e ms o dis u bances ha ha e no been con empla ed in he he mal balances, such as punc ual
e o s in he measu emen s, i egula ope a ions in he eac o o empe a u e o cul u e medium
o eplacemen . On he o he hand, he calib a ion by means o gene ic algo i hms allows o ob-
ain mean alues o pa ame e s used in he equa ions ha a e subjec ed o unce ain y, as hey a e
in lumped-pa ame e s ep esen a ions o balances ha should equi e dis ibu ed pa ame e ep e-
sen a ions and hus a e in gene al di icul o ob ain om ables. In gene al, he esul s ob ained
ha e been posi i e and no able o he use o he model in he de elopmen o mic oalgae g ow h
models whe e i s dynamics and o he pa ame e s such as p oduc i i y, pe o mance, consump ion
o CO2, and e olu ion o pH a e es ima ed.
The esul s o he empe a u e analysis o he cul i a ion o mic oalgae in Alme ía using
he empe a u e model o aceway eac o s ha e de e mined ha Scenedesmus alme iensis and
Dunaliella e iolec a mic oalgae a e sui able o p oduc ion du ing mos pa o he yea , espe-
cially du ing summe , due o i s high empe a u e index. Bo h Chlo ella py enoidosa and Spi ulina
pla ensis s ains a e also sui able o cul i a ion du ing he sp ing, summe and au umn pe iods,
due o a good empe a u e index beha iou bu less sui able han hose desc ibed abo e. On he
o he hand, he mic oalgae Nannochlo opsis oceanica is no capable o wi hs anding he empe -
a u es eached du ing la e sp ing and summe pe iods, being a mic oalgae di icul o cul i a e in
hese pe iods, bu being he mos sui able o cul i a ion in au umn and win e because i shows
he highes empe a u e index o all s ains o his seasonal pe iod.
The en i onmen al condi ions depend on he wea he and can be e y di e en om one season
o ano he . This ac has been aken in o accoun in he calib a ion o he model so ha i can adjus
o all he en i onmen al condi ions o each mon h, wi hou changing he pa ame e s o inc easing
he model complexi y. On he o he hand, being a model designed o all mon hs o he yea , he e
a e ce ain e o s due o a gene aliza ion o pa ame e s, bu a adeo be ween pe o mance and
complexi y has been ound.
22
The empe a u e es ima ion is eally use ul in he mic oalgae p oduc ion p ocess. The em-
pe a u e model can be combined wi h exis ing mic oalgae biomass p oduc ion models o add he
e ec o empe a u e on g ow h and hus make mo e accu a e and comple e mic oalgae p oduc ion
models. On he o he hand, empe a u e es ima ion can be used as a design ool when ins alling
a eac o in a de e mined loca ion. F om he g ow h p oduc i i y model and he en i onmen al
condi ions, i is possible o es ima e he empe a u e o a eac o in ha a ea and es ablish i s max-
imum biomass p oduc ion o he mic oalgae s ain iabili y. In his way, i is possible o assess he
sui abili y o ins all a aceway eac o in any speci ic a ea o es ablish di e en mic oalgae cul u es
depending on he season. Mo eo e , i can also be used o design con ol algo i hms o op imize
he eac o empe a u e.
Conclusions
This wo k p esen s a empe a u e model o aceway eac o s based on a he mal balance om
measu able condi ions in he en i onmen . The esul s o he dynamic empe a u e e olu ion ob-
ained om he model show sa is ac o y pe o mance ha closely esemble he ac ual empe a u e
alues, measu ed in he eac o . The g ea impac o empe a u e on he p oduc i i y o mic oalgae
has been demons a ed in he li e a u e and, he e o e, his ype o models has a undamen al ole in
he de elopmen o new and mo e comple e models o mic oalgae ha allow us o ully unde s and
all he pa ame e s ha a ec i s g ow h. The use o indus ial scale models ha ake in o accoun
all he a iables a ec ing he mic oalgae g ow h is sca ce in p ac ice, and hus, his empe a u e
model aims o complemen he use o mo e comple e models ha allow he de elopmen o p ecise
e alua ion applica ions in he ield o mic oalgae, such as op imal eac o con ol, a iable impac
s udies, pe o mance imp o emen o pa ame e es ima ion. In u u e wo k, he use ulness o he
model o es ima e he p oduc i i y o mic oalgae om di e en condi ions will be analyzed, in
addi ion o i s use as a design ool.
23
Acknowledgemen
This wo k has been pa ially unded by he ollowing p ojec s: DPI2017 84259-C2-1-R ( inanced
by he Spanish Minis y o Science and Inno a ion and EU-ERDF unds), and he Eu opean
Union’s Ho izon 2020 Resea ch and Inno a ion P og am unde G an Ag eemen No. 727874
SABANA.
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