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Carbon dioxide fluxes increase from day to night across European streams

Abstract

Globally, inland waters emit over 2 Pg of carbon per year as carbon dioxide, of which the majority originates from streams and rivers. Despite the global significance of fluvial carbon dioxide emissions, little is known about their diel dynamics. Here we present a large-scale assessment of day- and night-time carbon dioxide fluxes at the water-air interface across 34 European streams. We directly measured fluxes four times between October 2016 and July 2017 using drifting chambers. Median fluxes are 1.4 and 2.1 mmol m−2 h−1 at midday and midnight, respectively, with night fluxes exceeding those during the day by 39%. We attribute diel carbon dioxide flux variability mainly to changes in the water partial pressure of carbon dioxide. However, no consistent drivers could be identified across sites. Our findings highlight widespread day-night changes in fluvial carbon dioxide fluxes and suggest that the time of day greatly influences measured carbon dioxide fluxes across European streams.

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Carbon dioxide fluxes increase from day to night across European streams

Author: Attermeyer, Katrin,Casas-Ruiz, Joan Pere,Fuss, Thomas,Pastor, Ada,Cauvy-Fraunié, Sophie,Sheath, Danny,Nydahl, Anna C.,Doretto, Alberto,Portela, Ana Paula,Doyle, Brian C.,Simov, Nikolay,Gutmann Roberts, Catherine,Niedrist, Georg H.,Timoner, Xisca,Evtimova
Publisher: Nature Research
Year: 2021
Source: https://repositorio.ulisboa.pt/bitstream/10451/49425/1/s43247-021-00192-w.pdf
ARTICLE
Ca bon dioxide fluxes inc ease om day o nigh
ac oss Eu opean s eams
Ka in A e meye 1,2,3✉, Joan Pe e Casas-Ruiz 4,5, Thomas Fuss6, Ada Pas o 4,5,34, Sophie Cau y-F aunié7,
Danny Shea h8,35, Anna C. Nydahl1, Albe o Do e o9,10, Ana Paula Po ela 11,12, B ian C. Doyle13,
Nikolay Simo 14, Ca he ine Gu mann Robe s8, Geo g H. Nied is 15, Xisca Timone 4,5, Vesela E imo a 16,
Lau a Ba al-F aga5, Tea Bašić8,36, Joachim Aude 17,37, Anne Deininge 18,38, Geo gina Buss 8,
S e ano Fenoglio 10,19, Nú ia Ca alán 4,5,39,40, El i a de Ey o 20, F ancesca Pilo o 18,41,
Jo di-René Mo 4,21, Juliana Mon ei o22, Da id Fle che 8, Ch is ian Noss23, Mi iam Colls4,5,
Magdalena Nagle 24, Liu Liu 23,25, Cla a Rome o González-Quijano26, Fe an Rome o4,5, Nina Pansch25,
José L. J. Ledesma 17,27,28, Josephine Pegg 8,29, Ma cus Klaus18,42, Anna F eixa 4,5,
Sonia He e o O ega25, Cla a Mendoza-Le a 7,23, Adam Bednařík30,43, Jé émy A. Fon ielle25,
Pe e J. Gilbe 31, Lyubomi A. Kende o 32, Ma in Rulík30 & Pascal Bodme 23,33,44
Globally, inland wa e s emi o e 2 Pg o ca bon pe yea as ca bon dioxide, o which he
majo i y o igina es om s eams and i e s. Despi e he global significance o flu ial ca bon
dioxide emissions, li le is known abou hei diel dynamics. He e we p esen a la ge-scale
assessmen o day- and nigh - ime ca bon dioxide fluxes a he wa e -ai in e ace ac oss 34
Eu opean s eams. We di ec ly measu ed fluxes ou imes be ween Oc obe 2016 and July
2017 using d i ing chambe s. Median fluxes a e 1.4 and 2.1 mmol m−2h−1a midday and
midnigh , espec i ely, wi h nigh fluxes exceeding hose du ing he day by 39%. We a i-
bu e diel ca bon dioxide flux a iabili y mainly o changes in he wa e pa ial p essu e o
ca bon dioxide. Howe e , no consis en d i e s could be iden ified ac oss si es. Ou findings
highligh widesp ead day-nigh changes in flu ial ca bon dioxide fluxes and sugges ha he
ime o day g ea ly influences measu ed ca bon dioxide fluxes ac oss Eu opean s eams.
h ps://doi.o g/10.1038/s43247-021-00192-w OPEN
A lis o au ho a filia ions appea s a he end o he pape .
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Inland wa e s a e impo an sou ces o a mosphe ic ca bon
dioxide (CO
2
) pa ially o se ing he e es ial ca bon sink1,2.
S eams and i e s he ein ep esen majo CO
2
emi e s3.
Flu ial CO
2
fluxes a e p ima ily con olled by he gas exchange
eloci y a he wa e -ai in e ace (k) and he g adien be ween he
wa e and a mosphe ic pa ial p essu es o CO
2
(pCO
2
)4. Bo h
pa ame e s a e highly a iable in space and ime5,6, causing
unce ain y in he magni ude o egional and global flu ial CO
2
emissions2.
The high spa io empo al a iabili y o kand wa e pCO
2
can be
a ibu ed o a complex in e play o unde lying con ols. While k
in s eams is mos ly d i en by wa e u bulence c ea ed by a -
ia ions in flow and s eam mo phology7, he wa e pCO
2
is
influenced by he deg ee o hyd ological connec i i y be ween he
s eam and he adjacen ipa ian soils8as well as by in-s eam
p ocesses (e.g., s eam me abolism). The supply o CO
2
om
ex e nal sou ces, such as soil wa e o g oundwa e , in o s eams,
a ies wi h each and season5,9. Fu he mo e, seasonal and diel
changes in s eam pCO
2
a e a ibu ed o s eam me abolism
d i en by empe a u e and sola adia ion10–13. Ecosys em
espi a ion, a sou ce o CO
2
in he s eam, akes place h oughou
he whole day, and g oss p ima y p oduc ion, a sink o CO
2
,
occu s only du ing dayligh . Tempe a u e and sola adia ion also
di ec ly influence wa e pCO
2
, he o me by changing he solu-
bili y o he gas and he la e due o pho omine aliza ion14.
Howe e , ques ions emain ega ding he magni ude and ela i e
d i e s o seasonal and diel fluc ua ions o CO
2
fluxes in s eams.
P esen ly, mos flu ial CO
2
emission alues a e de i ed om k
es ima es based on wa e eloci y and s eam channel slope and
on wa e pCO
2
alues indi ec ly calcula ed om alkalini y, pH,
and empe a u e3. This app oach ails o cap u e he high spa-
io empo al a iabili y obse ed o kand pCO
2
and he e o e can
p o ide imp ecise es ima es o CO
2
fluxes15,16. Di ec field
obse a ions p o ide he means o imp o e es ima es and
unde s anding o he d i e s behind spa io empo al a iabili y,
and hus he dynamics o CO
2
ou gassing om unning wa e s.
Howe e , besides mos ly local s udies ha indi ec ly in e CO
2
fluxes om pCO
2
and k11,12,17,18, no di ec measu emen s exis
ha compa e day- ime and nigh - ime CO
2
fluxes om s eams
on a la ge spa ial scale.
The aim o his s udy was o assess he magni ude and d i e s
o s eam CO
2
flux a ia ions be ween day and nigh ac oss
Eu opean s eams. We hypo hesized ha CO
2
fluxes would di e
be ween day and nigh due o diel a ia ions in e es ial ino -
ganic ca bon inpu s, in si u me abolism, and empe a u e. As
highe empe a u es and sola adia ion may d i e di e ences in
pCO
2
, we expec ed a highe di e ence be ween day- ime and
nigh - ime fluxes wi h wa me empe a u es and a lowe la i-
udes. Hence, we measu ed day- ime and nigh - ime fluxes o
CO
2
a ou di e en pe iods h oughou one yea om
34 s eams (S ahle s eam o de s om 1 o 6) in 11 coun ies
ac oss Eu ope ollowing a s anda dized p ocedu e. CO
2
fluxes
we e measu ed s a ing a midday (11 a.m. G eenwich Mean
Time (GMT)) and midnigh (11 p.m. GMT) wi h d i ing flux
chambe s equipped wi h CO
2
senso s as desc ibed in Bas iken
e al.19. In he majo i y o he Eu opean s eams, we ound
inc eased CO
2
fluxes a he wa e –ai in e ace in he nigh
compa ed o he day wi h a median inc ease o 0.5 mmol m−2
h−1. Mos o he obse ed CO
2
flux a iabili y was explained by
changes in pCO
2
om day o nigh wi h mo e p onounced
changes a lowe la i udes.
Resul s and discussion
Magni ude o CO
2
flux a ia ion om day o nigh . Midday
CO
2
fluxes a he wa e –ai in e ace anged om −2.7 (up ake)
o 19.9 mmol m−2h−1(emission) (1.4 [0.5, 3.1]; median [in e -
qua ile ange (IQR)]; n=107) and midnigh fluxes anged om
−0.3 o 25.6 mmol m−2h−1(2.1 [0.9, 3.7]; n=107) (Fig. 1a;
Supplemen a y Table S3). Ou measu ed fluxes a e compa able o
o he s udies conduc ed in empe a e and bo eal s eams ha
used chambe s20,21 o empi ical models12,22,23, al hough hey
we e in he lowe ange o he numbe s modeled in a s udy in he
USA23 (Supplemen a y Fig. S2). The lowe numbe s migh be due
o he lack o ibu a y inflows, la ge woody deb is, and s ong
hyd aulic jumps in he selec ed s eam sec ions (Supplemen a y
Sampling manual).
To assess s eam CO
2
flux a ia ions be ween day and nigh ,
we compu ed he di e ence o nigh - ime minus day- ime fluxes
o each s eam and sampling pe iod, whe e posi i e numbe s
indica e an inc ease om day o nigh and ice e sa (Fig. 1b).
Di e ences in CO
2
fluxes amoun ed o 0.5 mmol m−2h−1[0.1,
1.4] (n=107) ac oss all si es and sampling pe iods, which is
equi alen o a ela i e inc ease o 39% [4%, 100%] (n=101; n
educed due o exclusion o ela i e compa isons o ze o flux a
day- ime) (Fig. 2). Al oge he , hese esul s poin owa ds a high
ele ance o nigh - ime CO
2
fluxes as epo ed ea lie o single
p e-alpine s eams12, s eam ne wo ks13,17 o i e s18, and in a
ecen compila ion o diel CO
2
da a om 66 s eams wo ldwide24.
A ough annual ex apola ion o fluxes om ou s udy si es
(Supplemen a y Me hods) shows ha he inclusion o nigh - ime
fluxes inc eases annual es ima es o si e-specific s eam CO
2
emissions by 16% [6%; 25%] (Supplemen a y Table S4). Hence,
ou measu emen s and he simplified ex apola ion o ou da a
emphasize he need o collec and in eg a e nigh - ime CO
2
flux
da a in o sampling p o ocols as well as egional upscaling e o s.
Looking in o he indi idual compa isons, we ound 83
inc eases in median CO
2
fluxes om day o nigh wi h se en
compa isons whe e he s eam e en swi ched om a sink o a
sou ce o CO
2
o he a mosphe e (Supplemen a y Table S3).
Howe e , we also ound ou compa isons whe e median CO
2
fluxes a day and nigh we e he same and 20 dec eases in he
nigh (Supplemen a y Table S3). These esul s and also o he
s udies13,25,26 sugges ha he di ec ion and s eng h o diel pCO
2
pa e n can be la gely a iable ac oss space and ime.
Diel CO
2
flux di e ences a y as a unc ion o la i ude and
wa e empe a u e. The diel di e ences in CO
2
fluxes we e sig-
nifican ly nega i ely ela ed o la i ude (Table 1A), wi h sub-
s an ial diel a ia ion mo e likely a lowe la i udes. Likewise, he
in e ac ion wi h la i ude and he wa e empe a u e was sig-
nifican (Table 1A), which migh be explained by highe em-
pe a u es a lowe la i udes du ing he sampling pe iods and
highe sola adia ion boos ing in-s eam p ima y p oduc ion27.
This da ase is de i ed om only 34 s eams dis ibu ed ac oss
di e en clima e zones in Eu ope. Howe e , o ou knowledge, i
is cu en ly he la ges s udy o i s kind, using flux chambe s o
measu e CO
2
fluxes, and compa e hose fluxes a day- ime and
nigh - ime on such a spa ial scale.
We ound no significan di e ences in he magni ude o diel
di e ences in CO
2
fluxes ela ed o wa e empe a u e (Table 1A)
using a linea mixed-e ec model (LME). Howe e , compa ing he
CO
2
fluxes a midday o midnigh a he di e en sampling pe iods,
we de ec ed significan diel changes in CO
2
fluxes in Oc obe ,
Janua y, and Ap il (Fig. 1a). Con a y o ou expec a ion ha highe
di e ences can be expec ed a highe empe a u es, we did
no de ec significan changes om day o nigh in July (Fig. 1a),
du ing which pe iod he lowes changes in absolu e numbe s we e
eco ded (0.3 mmol m−2h−1;Fig.1b). The highes di e ences o
CO
2
fluxes om day o nigh we e measu ed du ing Ap il
(1.1 mmol m−2h−1), ollowed by Janua y (0.5 mmol m−2h−1)
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and Oc obe (0.5 mmol m−2h−1). Lowe day-nigh changes in July
could be explained by inc eased ipa ian shading educing
pho osyn hesis28,29. Fo example, educed in-s eam pho osyn hesis
in summe compa ed o sp ing has been shown o a subalpine
s eam ne wo k29 o a empe a e o es ed headwa e s eam28.
Howe e , compa ing he canopy co e o he s eams and he
di e ences in CO
2
fluxes om day o nigh (Supplemen a y
Fig. S3h) e ealed no clea pa e n. A p obable al e na e explana ion
is ha CO
2
p oduc ion ia pho omine aliza ion du ing he day
coun e ac ed a dec ease ia CO
2
fixa ion by pho osyn hesis30 and
diminished diel pCO
2
and ul ima ely CO
2
flux changes. This
highligh s he complex in e play be ween di e en ligh -dependen
p ocesses in s eams influencing pCO
2
on a diel scale.
The impo ance o yea - ound measu emen s is highligh ed by
he Janua y da a se con aining he second-highes diel CO
2
flux
changes. Eu opean ice- ee s eams may be pe cei ed “do man ”
du ing hese pe iods and ep esen a i e CO
2
flux es ima es a e
hus o en missing3. Ou Janua y da a showed a magni ude o flux
compa ed o he es o he yea ac oss he Eu opean s eams as
well as high diel a iabili y in CO
2
fluxes (Fig. 1). This may be
a ibu ed in pa o he la i udinal co e age o ou s udy as we
included s eams om he bo eal o he Medi e anean. Fo
example, he wa e empe a u es o he Spanish s eams we e s ill
ela i ely high in win e wi h a ound 2.8–9.5 °C du ing he day
whe eas Swedish s eams showed hese empe a u es in Oc obe
and Ap il. A s udy in he co e minous US looking in o s eam
pCO
2
a iabili y also epo s a ying s eng hs o diel pCO
2
a iabili y, dependen on he in es iga ed s eam and ime25.
Hence, diel pCO
2
and CO
2
flux a iabili y can be la ge in s eams
o he no he n hemisphe e, s essing he need o un a el he si e-
specific d i e s o and mechanisms behind hese diel changes.
Fig. 1 Day- o-nigh changes o CO
2
fluxes a he wa e –ai in e ace o he sampled Eu opean s eams. S eam CO
2
fluxes (in mmol CO
2
m−2h−1)a
day- ime (yellow) and nigh - ime (blue) (a) and he calcula ed changes om nigh minus day (ΔCO
2
flux) (b) o all da a and sepa a ely o each sampling
pe iod. In he sampling pe iods compa isons in (a), CO
2
fluxes o indi idual s eam si es a e indica ed by ed (day) and ligh blue (nigh ) do s. The
boxplo s isualize he median o all s eam si es (line), he fi s and hi d qua iles (hinges), he 1.5*in e -qua ile anges (whiske s), and he ou lie s
ou side he ange o 1.5*in e -qua ile anges (black do s). On op o (a) a e p alues e ie ed om pai ed compa isons o median CO
2
fluxes es ed by
Wilcoxon signed- ank es s and he sample size (n). Significan p alues wi h p< 0.05 a e in bold wi h an as e isk. The di e ences in he CO
2
fluxes (b)in
mmol CO
2
m−2h−1 om day o nigh a e o Oc obe : 0.5 [0.1, 1.2]; Janua y: 0.5 [0.3, 0.9]; Ap il: 1.1 [0.1, 2.3]; July: 0.3 [−0.2, 1.1] (median [IQR]).
Fig. 2 Rela i e changes in CO
2
fluxes om day o nigh o all da a
oge he and o each sampling pe iod. A posi i e alue indica es an
inc ease in CO
2
fluxes du ing he nigh and ice e sa (exp essed as a
%-change o he day ime alues). Ou lie s (>1.5*IQR) we e excluded o
illus a ion pu poses as he la ge ela i e a ia ion in hese fluxes was due o
mino absolu e a ia ion in fluxes close o ze o. The median ela i e changes
we e posi i e h oughou all sampling pe iods, anging om 32% [0.6%, 95%]
in Oc obe , 38% [16%, 50%] in Janua y, 60% [7%, 177%] in Ap il, o 24%
[−16%, 69%] in July (median [IQR]; n=26, 21, 28, and 26, espec i ely).
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Diel CO
2
flux a iabili y d i en by changes in wa e pCO
2
.To
unde s and he mechanisms behind he obse ed changes in CO
2
fluxes om day o nigh , we fi s selec ed he wo p ima y con-
ols o CO
2
fluxes a he wa e –ai in e ace, i.e., he gas exchange
eloci y and wa e pCO
2
and explo ed he influence o hese
pa ame e s on absolu e CO
2
flux changes using an LME. The diel
CO
2
flux a iabili y in Eu opean s eams could be mos ly
a ibu ed o changes in wa e pCO
2
(Table 1B), whe eas changes
in he gas exchange eloci y kappea ed less impo an . In ac , we
did no measu e significan a ia ions in k om day o nigh in
ou s eams (Fig. 3; Supplemen a y Fig. S4h). Al hough diel
a iabili ies o gas exchange eloci ies ha e been epo ed o CO
2
and o he gases31,32, he majo i y o he in es iga ed s eams in
his s udy did no show hose changes. The pCO
2
as a majo
d i e o diel CO
2
flux a iabili y was also iden ified by a global
compila ion o high- equency CO
2
measu emen s24. Conse-
quen ly, i no majo changes in physical d i e s o gas exchanges
occu ha s ongly a ec he u bulence, such as hea y ain
e en s, i is su ficien o ocus on pCO
2
o assessing diel flux
changes a he wa e –ai in e ace.
In a second s ep, we es ed he influence o biogeochemical
pa ame e s ha a y on a diel scale on wa e pCO
2
day- o-nigh
di e ences (Table 1C). This LME iden ified a link be ween he
day- o-nigh changes in wa e pCO
2
and wa e dissol ed O
2
, wi h
pCO
2
gene ally inc easing and O
2
dec easing om day o nigh
(Supplemen a y Fig. S4b, c). This po en ially eflec s a diel cycle
o CO
2
con olled by aqua ic p ima y p oduc ion and espi a ion
(in-s eam me abolism). Hence, e en hough in si u me abolism
may play a mino ole in de e mining he baseline pCO
2
and flux
in smalle s eams (mos ly con olled by e es ial inpu s23), ou
esul s sugges ha me abolism can be an impo an d i e o he
diel fluc ua ions in CO
2
fluxes. Indeed, inc eased wa e pCO
2
du ing he nigh has been a ibu ed o a dec ease in CO
2
fixa ion
by p ima y p oduce s13,18,24, al hough a ecen s udy sugges s
ha he adjacen g oundwa e can also show measu able bu less
p onounced diel pCO
2
a ia ions33. P e ious esea ch sugges s
ha in si u mine aliza ion o CO
2
should play a la ge ole in CO
2
dynamics in la ge s eams because hey a e less influenced by
ex e nal CO
2
sou ces23. Ne e heless, we did no find any end in
CO
2
flux day- o-nigh di e ences wi h s eam wid h o discha ge
as a p oxy o size (Supplemen a y Fig. S3c, ) o wi h s eam
o de (Supplemen a y Fig. S5) al hough o he s udies sugges
change o e a size g adien 23,34. Fu he mo e, he LME es ing
hyd omo phological and ca chmen a iables on pCO
2
day- o-
nigh di e ences (Table 1D) did no e eal significan ela ion-
ships wi h ei he o hese d i e s. This could ei he be due o he
ac ha we missed he bes p oxy ha de e mines day- o-nigh
di e ences in pCO
2
in Eu opean s eams o ha he e a e no
common d i e s among he in es iga ed s eams. La ge diel
a iabili y o CO
2
pa e ns wi hin one Swedish s eam26 o
among US headwa e s eams25 ha e been desc ibed, which
complica es he iden ifica ion o gene al d i e s. Hence, u he
esea ch is needed o deciphe he diel a iabili y o he sou ces
and dynamics o pCO
2
in s eams and o unde s and he
en i onmen al, hyd omo phological, and ca chmen d i e s
be o e hei impo ance on a egional o global scale can be
assessed.
In-s eam me abolism wi h pho osyn he ic CO
2
fixa ion
diminishing pCO
2
du ing he day may explain he inc ease in
CO
2
fluxes om day o nigh , bu canno explain why in some
ins ances we measu ed a lowe CO
2
flux a nigh . Po en ial
explana ions o a lowe nigh flux migh include: (i) highe
a mosphe ic CO
2
concen a ions due o he absence o e es ial
CO
2
fixa ion du ing nigh and he e o e a lowe
wa e –a mosphe e pCO
2
g adien , (ii) pho omine aliza ion o
Table 1 Resul s o he linea mixed-e ec models (LME).
Response
a iable
Fixed e ec χ2(1) pSign
(A) Tes ing spa ial and empo al hypo heses
CO
2
flux
di e ence
om day
o nigh
La i ude 7.4207 0.006 −
Wa e
empe a u e (day)
0.0168 0.897
Wa e empe a u e
(day)*la i ude
4.9594 0.026 +
(B) Tes ing physical and biogeochemical d i e s o CO
2
flux changes
CO
2
flux
di e ence
om day
o nigh
ΔWa e pCO
2
4.9497 0.026 +
ΔGas ans e
eloci y k
0.5613 0.454
(C) Tes ing biogeochemical d i e s o pCO
2
changes
pCO
2
di e ence
om day
o nigh
ΔWa e O
2
concen a ion
7.9879 0.005 −
ΔpH 0.0345 0.853
ΔConduc i i y 0.0293 0.864
ΔT
w
−T
a
a(p oxy o
hea flux)
1.6720 0.196
ΔWa e empe a u e 0.8731 0.350
(D) Tes ing ca chmen and hyd omo phological d i e s o pCO
2
changes
pCO
2
di e ence
om day
o nigh
Day leng h 1.7244 0.189
S eam we ed wid h 0.3748 0.540
Discha ge 3.4458 0.063
% o es 0.0950 0.758
Ca chmen a ea 2.3656 0.124
aHea flux calcula ed as wa e empe a u e (T
w
) minus ai empe a u e (T
a
).
(A) Ma ginal R2=0.12, condi ional R2=0.18, sample size =107.
(B) Ma ginal R2=0.08, condi ional R2=0.10, sample size =77.
(C) Ma ginal R2=0.13, condi ional R2=0.33, sample size =78.
(D) Ma ginal R2=0.11, condi ional R2=0.13, sample size =68.
The e ec s o la i ude and wa e empe a u e du ing he day (A) and he e ec o day- o-nigh
di e ences o pCO
2
and he gas ans e eloci y (Δ=nigh minus day alues) (B) on he day-
o-nigh di e ence o CO
2
fluxes we e es ed. Fu he mo e, he e ec o day- o-nigh di e ences
o physical and biogeochemical pa ame e s (C) and he e ec o ca chmen and
hyd omo phological ela ed pa ame e s (D) on he day- o-nigh di e ences o pCO
2
we e
e alua ed. S eam ID was included as a andom e ec on he in e cep . Significances o fixed
e ec s we e assessed wi h likelihood a io es s wi h deg ees o eedom =1. The slope
di ec ion (sign) o he e ec is indica ed wi h –o +when significan . Significan p alues <
0.05 a e in bold.
Fig. 3 Diel changes in CO
2
fluxes (FCO
2
) and o he physical and chemical
pa ame e s o Oc obe /Janua y/Ap il and July, espec i ely. The
physical and chemical pa ame e s comp ise a mosphe ic CO
2
(Ai CO
2
),
he di e ences o CO
2
concen a ions in he wa e minus he ai (CO
2
g adien
), he wa e –ai gas ans e eloci y (k), he di e ences o
empe a u es in he wa e minus he ai (T
w
−T
a
), he wa e empe a u e
(WT), he oxygen concen a ion in he wa e (O
2
), pH in he wa e , he
pa ial p essu e o CO
2
in he wa e (pCO
2
), and conduc i i y (Cond). The
a ows indica e significan inc eases (↑) o significan dec eases (↓) om
day o nigh and he line indica es no significan change (―) es ed by a
Wilcoxon signed- ank es (see Supplemen a y Fig. S4 o mo e
in o ma ion). The di e ences be ween he sampling pe iods Oc obe /
Janua y/Ap il and July, espec i ely, de ec ed in his Eu opean s udy a e
highligh ed in ed.
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o ganic ma e o CO
2
coun e ac ing he CO
2
fixa ion by p ima y
p oduce s du ing day- ime, and (iii) lowe u bulence due o a
dec ease in s eam discha ge in he nigh . We ound significan
inc eases in a mosphe ic CO
2
close o he in es iga ed s eams a
nigh . Howe e , his was usually accompanied by concomi an
inc eases in wa e pCO
2
and he e o e did no ansla e in o
smalle CO
2
g adien s be ween he wa e –ai in e ace (Fig. 3;
Supplemen a y Fig. S4b, e, i). P oduc ion o CO
2
due o
pho omine aliza ion o dissol ed o ganic ca bon (DOC) could
play a ole in diel CO
2
dynamics in s eams wi h high amoun s o
colo ed e es ial o ganic ma e 35. In he highly colo ed s eams,
diel CO
2
pa e ns can addi ionally be influenced by DOC shading
diminishing ben hic p ima y p oduc ion36. In Oc obe , we
measu ed DOC concen a ions in a subse o he in es iga ed
s eams o ano he s udy37 whe e an ag icul u al s eam in
Sweden and pea land-domina ed s eams in G ea B i ain had
high DOC concen a ions (>10 mg L−1) whe eas he median
DOC was much lowe wi h 2.6 mg L−137. Due o he limi ed da a,
we could no es he e ec o DOC on pCO
2
changes and we can
nei he confi m no exclude ha pho omine aliza ion migh play
a ole o diel pCO
2
and consequen ly CO
2
flux a iabili y in he
s udied s eams. We did find, none heless, ha he majo i y o he
s eams whe e CO
2
fluxes we e lowe du ing he nigh also had a
lowe gas ans e eloci y (k
600
), likely due o a sligh dec ease in
s eam discha ge and he e o e u bulence. Thus, while he e was
a gene al endency o inc eased pCO
2
om day o nigh (only 4
ou o 20 dec eases in CO
2
fluxes om day o nigh showed a
concomi an dec ease in wa e pCO
2
), indi idual s eams a single
ime poin s seemed o expe ience diel fluc ua ions in discha ge as
desc ibed elsewhe e38. This can simul aneously educe he gas
exchange eloci y o he s eam and he e o e cause lowe nigh -
ime CO
2
fluxes. In his s udy, we only measu ed s eam
discha ge du ing he day, and he e o e he impo ance o his
mechanism emains o be confi med.
Maximum CO
2
flux di e ences migh be e en highe —lim-
i a ions o he s udy design. Fo o ganiza ional easons, he
sampling scheme o his collabo a i e s udy was s anda dized o
fixed imes o measu emen s o he day and he nigh . All eams
ac oss Eu ope s a ed hei measu emen s a 11:00 (midday) and
23:00 GMT (midnigh ) du ing each sampling pe iod, which has
consequences o he magni ude o he obse ed diel a iabili y o
he CO
2
fluxes. The la ges diel di e ences in s eam pCO
2
ha e
gene ally been de ec ed a he end o he day compa ed o he end
o he nigh 12,18,39. In an ag icul u al Swedish s eam, diel max-
imum and minimum CO
2
concen a ions we e eached a 04:00
and 16:00 (GMT), espec i ely, du ing sp ing and ea ly summe
pe iods (la e Ap il o ea ly July) whe e diel dynamics we e mos
p onounced26. In hese scena ios, sampling midday and mid-
nigh , as conduc ed in his s udy, would be close o hose maxima
and minima as hey can be eached al eady ea lie du ing he day
(see Supplemen a y Fig. S6 in May). Howe e , he maxima and
minima o diel CO
2
dynamics in s eams can a y la gely (see
Supplemen a y Fig. S6 in Oc obe , Ap il, July). In ano he
example o Ge man s eams39, he imes o minima and maxima
di e be ween s eams and imes, and he fixed ime poin s
chosen in his s udy would miss he maximum di e ences ha
can be obse ed (see Supplemen a y Fig. S7 in Augus ). Hence,
ou es ima es could be conse a i e as we compa ed fixed ime
poin s a midday and midnigh . In gene al, CO
2
flux measu e-
men s in s eams a e highly sensi i e owa ds he ime o he day
because diel minimum and maximum o pCO
2
can a y la gely
om mon h o mon h bu also om day o day. As we ound ha
he diel a iabili y o pCO
2
was he majo d i e o diel CO
2
fluxes, we ecommend u u e s udies ha plan o measu e CO
2
fluxes di ec ly wi h he chambe me hod, o addi ionally moni o
he diel a iabili y o pCO
2
wi h logge s a a high empo al eso-
lu ion. This app oach will p o ide he oppo uni y o es ima e i
he measu emen s a e done du ing peak imes o no .
While ou esul s p o ide a fi s insigh in o he d i e s o day-
nigh di e ences in CO
2
fluxes, he high unce ain y in he
models as well as he some imes opposing pa e ns—inc eases
and dec eases om day o nigh in di e en s eams and
sampling pe iods—poin owa ds di e en d i e s a ying on a
empo al and spa ial scale. We ecommend ha u u e s udy
designs inco po a e high- equency CO
2
da a oge he wi h
biogeochemical a iables om he s eam (e.g., O
2
) and
he a mosphe e (e.g., CO
2
o empe a u e)40. Addi ionally, we
ecommend including adioac i e o s able ca bon iso ope
signa u es o ack po en ial sou ces o CO
2
and hei changes
in s eams41,42 o be e assess e es ial–aqua ic linkages.
Linking empo al pa e ns o flu ial CO
2
fluxes wi h hei d i e s
ac oss la ge spa ial scales is a pa h owa ds a mo e accu a e
unde s anding o hei ole in egional and global ca bon cycles.
Ou esul s demons a e ha , in many s eams ac oss Eu ope,
nigh - ime CO
2
fluxes exceed day- ime, esul ing in a po en ial
unde es ima ion o global CO
2
emissions om inland wa e s i
no conside ed. I is hus c i ical o accoun o he diel a iabili y
o flu ial CO
2
fluxes o accu a e daily and annual es ima es o
CO
2
emissions om inland wa e s.
Me hods
Sampling scheme. The p ojec included 16 eams dis ibu ed ac oss 11 Eu opean
coun ies. E e y eam sampled one o h ee s eams (Supplemen a y Table S1)
e e y 3 mon hs (Oc obe 2016/Janua y 2017/Ap il 2017/July 2017) wi hin a ime
ame o 2 weeks h oughou a whole yea . These sampling pe iods oughly co e
he seasons au umn/win e /sp ing/summe al hough, due o he la ge la i udinal
co e age o he sampling si es, he seasons and hei cha ac e is ics a y la gely. In
o al, 34 s eam si es (Supplemen a y Fig. S1) we e isi ed each sampling pe iod
du ing he specified 2 weeks’ ime ame excep o 11 s eams in Janua y ha we e
ozen du ing he sampling weeks (Supplemen a y Table S3).
CO
2
fluxes we e measu ed once e e y sampling pe iod wi h d i ing flux
chambe s equipped wi h CO
2
senso s. This me hod has p o en o be a eliable and
leas biased di ec measu emen o CO
2
fluxes a he wa e –ai in e ace in
s eams19,43.CO
2
concen a ions in he chambe headspace we e logged e e y 30 s
o e a pe iod o 5–10 min du ing each un, and CO
2
fluxes we e calcula ed based
on he a e o change o e ime in pCO
2
in he chambe headspace. A each s eam,
we measu ed CO
2
fluxes wi h he flux chambe (fi e imes), pCO
2
in he
a mosphe e and wa e wi h he CO
2
senso s in he flux chambe (de ails desc ibed
in Supplemen a y Me hods), pH, empe a u e, conduc i i y, and oxygen in he
wa e wi h a mul ip obe (Supplemen a y Table S2). These measu emen s we e
s a ed a 11:00 and 23:00 (GMT) and las ed app oxima ely wo hou s and a e
e e ed o as midday and midnigh h oughou his a icle. S eam wid h, dep h,
canopy co e , and discha ge we e de e mined du ing he day (see Supplemen a y
Sampling manual o de ails). In addi ion, he ollowing in o ma ion was collec ed
o each s eam once du ing he s udy: s eam o de , clima e zone, ca chmen a ea
un il he endpoin o he in es iga ed s eam si e and he pe cen age o co e age o
di e en land use classes in his ca chmen a ea, and p edominan geology
(Supplemen a y Table S1).
Calcula ions o CO
2
fluxes and gas ans e eloci y. Flux a es we e ob ained
om he linea slopes o he pCO
2
in he chambe headspace o e ime and flux
was accep ed i he coe ficien o de e mina ion (R2) o he slope was a leas 0.6544.
An excep ion was made in cases whe e he slope was close o ze o and he pCO
2
in
he a mosphe e and wa e (measu ed a he same ime) we e a equilib ium. These
fluxes we e se o ze o. Final flux a es F(mmol CO
2
m−2h−1) we e calcula ed
acco ding o Eq. (1)45:
F¼S103PV
RTA 60 60;ð1Þ
whe e Sis he slope (ppm s−1), Pis he pCO
2
in he a mosphe e (a m), Vis he
olume (mL) o he d i ing chambe , Ris he gas cons an (82.0562 mL a m K−1
mol−1), Tis he chambe ai empe a u e (K), Ais he bo om a ea o he chambe
(m2), and he las e m is he con e sion om seconds o hou s. In his s udy, we
ollowed he sign con en ion whe eby posi i e alues indica e a CO
2
flux om he
s eam o he a mosphe e (sou ce) and nega i e alues indica e a flux om he
a mosphe e o he s eam (sink). The magni udes o a ia ions be ween day- ime
and nigh - ime measu emen s a e addi ionally s a ed as pe cen inc eases, which
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we e compu ed by di iding he di e ence be ween he alues a nigh minus day by
he alue a day and exp essing he esul as a pe cen change om day o nigh .
We used F(Eq.(1)) o calcula e he gas ans e eloci y (kin cm h−1)by
in e ing he equa ion o Fick’s law o gas di usion, acco ding o Eq. (2):
k¼F
kHðCO2wa e CO2ai Þ100;ð2Þ
whe e kH is Hen y’s cons an (in mol L−1a m−1) adjus ed o empe a u e46.
Fo compa ison o ans e eloci ies be ween si es and sampling pe iods and
wi h he li e a u e, k(Eq. ( 2)) was s anda dized o k
600
(Eq. (3)):
k600 ¼k600
Sc

0:5
ð3Þ
whe e kis he ans e eloci y a in si u empe a u e (T), Sc is he Schmid numbe
o in si u empe a u e T, he Schmid numbe o 20 °C in eshwa e is 600, and
ep esen ing a hyd odynamic ough wa e su ace ypical in s eams he exponen
o −0.5 was chosen47.
S a is ical analyses. All s a is ical analyses we e pe o med wi h median alues o
h ee o fi e floa ing chambe uns pe day and nigh , espec i ely, using he
s a is ical p og amming language R48 ( e sion 3.5.1). Samplings ha gene a ed less
han h ee alues o ei he day o nigh due o an R2o he slope <0.6544 we e
excluded om u he analysis educing he numbe om 136 o 107 day–nigh
compa isons. Fo ou s a is ical es s, he alpha le el was se o α=0.05. Significan
di e ences be ween day- ime and nigh - ime measu emen s o each sampling
pe iod ac oss all s eams we e es ed wi h Wilcoxon signed- ank es s49 whe e
median day- ime and nigh - ime alues o each s eam si e we e pai ed (Fig. 1a).
The same es s we e conduc ed o he o he biogeochemical a iables measu ed a
midday and midnigh (see Fig. 3; Supplemen a y Fig. S4).
Wi h a fi s linea mixed-e ec model (LME) we es ed he la i udinal and wa e
empe a u e e ec on CO
2
flux di e ences om day o nigh . A second LME was
buil o e alua e he wo majo d i e s o CO
2
flux di e ences om day o nigh :
pCO
2
and gas exchange eloci y (k). A hi d LME was subsequen ly used o
de e mine he biochemical ac o s po en ially influencing he di e ences o he
nigh - ime minus day- ime pCO
2
, which was iden ified as he only significan
d i e in he second LME. Finally, a ou h LME was buil o e alua e he e ec o
ca chmen and hyd omo phological pa ame e s on he day- o-nigh di e ences o
pCO
2
. Fo hese es s, we used he “lme ” unc ion o he R-package “lme4”50 wi h
maximum-likelihood es ima ion. Fixed e ec s o he LME wi h biogeochemical
pa ame e s o pCO
2
di e ences om day o nigh included absolu e di e ences
om day o nigh o oxygen concen a ion in he wa e , pH, conduc i i y,
empe a u e g adien o a mosphe e and wa e , and wa e empe a u e. Fixed
e ec s o he LME wi h ca chmen and hyd omo phological pa ame e s included
day leng h (i.e., sun hou s om sun ise o sunse ), s eam we ed wid h, discha ge,
% o es o he ca chmen , and ca chmen a ea. These a iables a e mos ly emo ely
a ailable o s eams. Fo he LMEs we included s eam ID as a andom e ec
allowing di e en in e cep s o each s eam o accoun o pseudo eplica ion (one
da a poin pe sampling pe iod pe s eam) and z-scaled all fixed e ec s wi h he
“scale” unc ion be o e unning he models. S a is ical significances o fixed e ec s
we e assessed wi h likelihood a io es s using he unc ion “d op1”51. The
espec i e LMEs we e ollowed by a model alida ion, checking he esiduals o
no mal dis ibu ion and homogenei y o a iances52. A sepa a ion o he da ase o
check i d i e s be ween inc eases om day o nigh and dec eases om day o
nigh di e did no e eal accep able models in e ms o model alida ion (i.e.,
esiduals we e no no mally dis ibu ed). Al hough ou da ase p o ided a la ge
spa ial co e age on day–nigh di e ences in CO
2
fluxes in Eu opean s eams, i did
no ha e he s a is ical powe o es o significan d i e s sepa a ely o inc eases
and dec eases.
Da a a ailabili y
The da a ha suppo he findings o his s udy a e openly a ailable in figsha e a h ps://
doi.o g/10.6084/m9.figsha e.12717188.
Code a ailabili y
This manusc ip includes no code.
Recei ed: 13 No embe 2020; Accep ed: 21 May 2021;
Re e ences
1. Bu man, D. E. e al. Aqua ic ca bon cycling in he con e minous Uni ed S a es
and implica ions o e es ial ca bon accoun ing. P oc. Na l. Acad. Sci. USA
113,58–63 (2016).
2. D ake, T. W., Raymond, P. A. & Spence , R. G. M. Te es ial ca bon inpu s o
inland wa e s: a cu en syn hesis o es ima es and unce ain y. Limnol.
Oceanog . Le 3, 132–142 (2018).
3. Raymond, P. A. e al. Global ca bon dioxide emissions om inland wa e s.
Na u e 503, 355–359 (2013).
4. MacIn y e,S.,Wanninkho ,R.&Chan on,J.P.T acegasexchangein
eshwa e and coas al ma ine sys ems: flux ac oss he ai wa e in e ace. In
Me hods in Ecology: Biogenic T ace Gases: Measu ing Emissions om Soil
and Wa e (eds Ma son, P. & Ha iss, R.) 52–97 (Blackwell Publishing,
1995).
5. Du e , C., Bu man, D. E., Ma x, A., Ribolzi, O. & Hu ley, L. B. CO
2
e asion
along s eams d i en by g oundwa e inpu s and geomo phic con ols. Na .
Geosci. 11, 813–818 (2018).
6. Roche ‐Ros, G., Sponselle , R. A., Lidbe g, W., Mö h, C. & Giesle , R.
Landscape p ocess domains d i e pa e ns o CO
2
e asion om i e
ne wo ks. Limnol. Oceanog . Le . 4,87–95 (2019).
7. Hall, R. O. & Ulse h, A. J. Gas exchange in s eams and i e s. WIREs Wa e
e1391 (2019). h ps://doi.o g/10.1002/wa 2.1391
8. Hope, D., Palme , S. M., Bille , M. F. & Dawson, J. J. C. Va ia ions in dissol ed
CO
2
and CH
4
in a fi s -o de s eam and ca chmen : an in es iga ion o
soil–s eam linkages. Hyd ol. P ocess. 18, 3255–3275 (2004).
9. Ho gby, Å., Gómez-Gene , L., Esco fie , N. & Ba in, T. J. Dynamics and
po en ial d i e s o CO
2
concen a ion and e asion ac oss empo al scales in
high-alpine s eams. En i on. Res. Le . 14, 124082 (2019).
10. Guasch, H., A mengol, J., Ma í, E. & Saba e , S. Diu nal a ia ion in dissol ed
oxygen and ca bon dioxide in wo low-o de s eams. Wa e Res. 32,
1067–1074 (1998).
11. Lynch, J. K., Bea y, C. M., Seidel, M. P., Jungs , L. J. & DeG andp e, M. D.
Con ols o i e ine CO
2
o e an annual cycle de e mined using di ec , high
empo al esolu ion pCO
2
measu emen s. J. Geophys. Res. 115, G03016
(2010).
12. Pe e , H. e al. Scales and d i e s o empo al pCO
2
dynamics in an Alpine
s eam. J. Geophys. Res. Biogeosci. 119, 1078–1091 (2014).
13. Roche -Ros, G., Sponselle , R. A., Be gs öm, A.-K., My s ene , M. & Giesle ,
R. S eam me abolism con ols diel pa e ns and e asion o CO
2
in A c ic
s eams. Glob. Chang. Biol 00,1–14 (2019).
14. Koehle , B., Landelius, T., Weyhenmeye , G. A., Machida, N. & T an ik, L. J.
Sunligh -induced ca bon dioxide emissions om inland wa e s. Glob.
Biogeochem. Cycles 28, 696–711 (2014).
15. Golub, M., Desai, A. R., McKinley, G. A., Remucal, C. K. & S anley, E. H.
La ge unce ain y in es ima ing pCO
2
om ca bona e equilib ia in lakes. J.
Geophys. Res. Biogeosci. 122, 2909–2924 (2017).
16. Raymond, P. A. e al. Scaling he gas ans e eloci y and hyd aulic geome y
in s eams and small i e s. Limnol. Oceanog . Fluids En i on. 2,41–53
(2012).
17. Schelke , J., Singe , G. A., Ulse h, A. J., Hengsbe ge , S. & Ba in, T. J. CO
2
e asion om a s eep, high g adien s eam ne wo k: impo ance o seasonal
and diu nal a ia ion in aqua ic pCO
2
and gas ans e . Limnol. Oceanog . 61,
1826–1838 (2016).
18. Reiman, J. H. & Xu, Y. J. Diel a iabili y o pCO
2
and CO
2
ou gassing om he
lowe Mississippi Ri e : implica ions o i e ine CO
2
ou gassing es ima ion.
Wa e 11, 43 (2019).
19. Bas iken, D., Sundg en, I., Na chimu hu, S., Reyie , H. & Gål alk, M.
Technical No e: cos -e ficien app oaches o measu e ca bon dioxide (CO
2
)
fluxes and concen a ions in e es ial and aqua ic en i onmen s using mini
logge s. Biogeosciences 12, 3849–3859 (2015).
20. Looman, A., Mahe , D. T., Pendall, E., Bass, A. & San os, I. R. The ca bon
dioxide e asion cycle o an in e mi en fi s -o de s eam: con as ing
wa e –ai and soil–ai exchange. Biogeochemis y 132,87–102 (2017).
21. C aw o d, J. T. e al. CO
2
and CH
4
emission om s eams: pa e ns, con ols,
and egional significance. Glob. Biogeochem. Cycles 28, 197–210 (2014).
22. Teodo u, C. R., Del Gio gio, P. A., P ai ie, Y. T. & Cami e, M. Pa e ns in
pCO
2
in bo eal s eams and i e s o no he n Quebec, Canada. Glob.
Biogeochem. Cycles 23, GB2012 (2009).
23. Ho chkiss, E. R. e al. Sou ces o and p ocesses con olling CO
2
emissions
change wi h he size o s eams and i e s. Na . Geosci. 8, 696–699 (2015).
24. Gómez-Gene , L. e al. Global ca bon dioxide e flux om i e s enhanced by
high noc u nal emissions. Na . Geosci.1–6 (2021). h ps://doi.o g/10.1038/
s41561-021-00722-3
25. C aw o d, J. T., S anley, E. H., Do nblase , M. M. & S iegl, R. G. CO
2
ime
se ies pa e ns in con as ing headwa e s eams o No h Ame ica. Aqua . Sci.
79, 473–486 (2016).
26. Wallin, M. B., Aude , J., Peacock, M., Sahlée, E. & Win e dahl, M. Ca bon
dioxide dynamics in an ag icul u al headwa e s eam d i en by hyd ology
and p ima y p oduc ion. Biogeosciences 17, 2487–2498 (2020).
27. Dema s, B. O. L. e al. Impac o wa ming on CO
2
emissions om s eams
coun e ed by aqua ic pho osyn hesis. Na . Geosci. 9, 758–761 (2016).
ARTICLE COMMUNICATIONS EARTH & ENVIRONMENT | h ps://doi.o g/10.1038/s43247-021-00192-w
6COMMUNICATIONS EARTH & ENVIRONMENT | (2021) 2:118 | h ps://doi.o g/10.1038/s43247-021-00192-w | www.na u e.com/commsen
28. Robe s, B. J., Mulholland, P. J. & Hill, W. R. Mul iple scales o empo al
a iabili y in ecosys em me abolism a es: esul s om 2 yea s o con inuous
moni o ing in a o es ed headwa e s eam. Ecosys ems 10, 588–606 (2007).
29. Ulse h, A. J., Be uzzo, E., Singe , G. A., Schelke , J. & Ba in, T. J. Clima e-
induced changes in sp ing snowmel impac ecosys em me abolism and
ca bon fluxes in an Alpine S eam Ne wo k. Ecosys ems 21, 373–390 (2018).
30. Co y, R. M., Wa d, C. P., C ump, B. C. & Kling, G. W. Sunligh con ols wa e
column p ocessing o ca bon in a c ic esh wa e s. Science (80-.) 345, 925–928
(2014).
31. Tobias, C. R., Böhlke, J. K., Ha ey, J. W. & Busenbe g, E. A simple echnique
o con inuous measu emen o ime‐ a iable gas ans e in su ace wa e s.
Limnol. Oceanog . Me hods 7, 185–195 (2009).
32. Be g, P. & Pace, M. L. Con inuous measu emen o ai –wa e gas exchange by
unde wa e eddy co a iance. Biogeosciences 14, 5595–5606 (2017).
33. Riml, J., Campeau, A., Bishop, K. & Wallin, M. B. Spec al decomposi ion
e eals new pe spec i es on CO
2
concen a ion pa e ns and soil-s eam
linkages. J. Geophys. Res. Biogeosci. 124, 3039–3056 (2019).
34. Liu, S. & Raymond, P. A. Hyd ologic con ols on pCO
2
and CO
2
e flux in US
s eams and i e s. Limnol. Oceanog . Le 3, 428–435 (2018).
35. Lindell, M. J., G anéli, H. W. & Be ilsson, S. Seasonal pho o eac i i y o
dissol ed o ganic ma e om lakes wi h con as ing humic con en . Can. J.
Fish. Aqua . Sci. 57, 875–885 (2000).
36. Ask, J., Ka lsson, J., Pe sson, L. & Ask, P. Te es ial o ganic ma e and ligh
pene a ion: e ec s on bac e ial and p ima y p oduc ion in lakes. Limnol.
Oceanog . 54, 2034–2040 (2009).
37. B a o, A. G. e al. The in e play be ween o al me cu y, me hylme cu y and
dissol ed o ganic ma e in flu ial sys ems: a la i udinal s udy ac oss Eu ope.
Wa e Res.144, 172–182 (2018).
38. Schwab, M., Klaus, J., Pfis e , L. & Weile , M. Diel discha ge cycles explained
h ough iscosi y fluc ua ions in ipa ian inflow. Wa e Resou . Res. 52,
8744–8755 (2016).
39. Bodme , P., Heinz, M., Pusch, M., Singe , G. & P emke, K. Ca bon dynamics
and hei link o dissol ed o ganic ma e quali y ac oss con as ing s eam
ecosys ems. Sci. To al En i on. 553, 574–586 (2016).
40. Vachon, D. e al. Pai ed O2–CO
2
measu emen s p o ide eme gen insigh s
in o aqua ic ecosys em unc ion. Limnol. Oceanog . Le .5, 287–294 (2019).
41. Campeau, A. e al. S able ca bon iso opes e eal soil-s eam DIC linkages in
con as ing headwa e ca chmen s. J. Geophys. Res. Biogeosci. 123, 149–167
(2018).
42. Campeau, A. e al. Cu en o es ca bon fixa ion uels s eam CO
2
emissions.
Na . Commun. 10,1–9 (2019).
43. Lo ke, A. e al. Technical no e: d i ing e sus ancho ed flux chambe s o
measu ing g eenhouse gas emissions om unning wa e s. Biogeosciences 12,
7013–7024 (2015).
44. T emblay, A., Va al y, L., Ga neau, M. & Roehm, C. G eenhouse Gas
Emissions-Fluxes and P ocesses: Hyd oelec ic Rese oi s and Na u al
En i onmen s (Sp inge Science & Business Media, 2005).
45. Duc, N. T. e al. Au oma ed flux chambe o in es iga ing gas flux a
wa e –ai in e aces. En i on. Sci. Technol. 47, 968–975 (2013).
46. Golden um, J. A. GHG Measu emen Guidelines o F eshwa e Rese oi s:
De i ed F om: he UNESCO/IHA G eenhouse Gas Emissions om F eshwa e
Rese oi s Resea ch P ojec (In e na ional Hyd opowe Associa ion (IHA),
2010).
47. Jähne, B. e al. On he pa ame e s influencing ai –wa e gas exchange. J.
Geophys. Res. Ocean. 92, 1937–1949 (1987).
48. R Co e Team. R: A Language and En i onmen o S a is ical Compu ing (R
Founda ion o S a is ical Compu ing, 2018).
49. Wilcoxon, F. Indi idual compa isons by anking me hods. Biome . Bull. 1,
80–83 (1945).
50. Ba es, D., Maechle , M., Bolke , B. & Walke , S. Fi ing linea mixed-e ec s
models using lme4. J. S a . So w. 67,1–48 (2015).
51. Zuu , A., Ieno, E. N., Walke , N., Sa elie , A. A. & Smi h, G. M. Mixed E ec s
Models and Ex ensions in Ecology wi h R (Sp inge Science & Business Media,
2009).
52. Zuu , A. F. & Ieno, E. N. A p o ocol o conduc ing and p esen ing esul s o
eg ession‐ ype analyses. Me hods Ecol. E ol. 7, 636–645 (2016).
Acknowledgemen s
We hank he ini ia o s o he fi s Collabo a i e Eu opean F eshwa e Science P ojec o
Young Resea che s, he Eu opean Fede a ion o F eshwa e Sciences (EFFS) boa d, he
Eu opean F esh and Young Resea che s (EFYR) and he ep esen a i es o he F esh
Blood o F esh Wa e (FBFW) mee ings. We also hank he se en na ional eshwa e
socie ies financing his p ojec , namely he Ibe ian Associa ion o Limnology (AIL; Spain
and Po ugal), Deu sche Gesellscha ü Limnologie e.V. (DGL; Ge many), Swiss Socie y
o Hyd ology and Limnology (SGHL; Swi ze land), I alian Associa ion o Oceanog aphy
and Limnology (I aly), F eshwa e Biological Associa ion (FBA; Uni ed Kingdom),
F ench Limnological Associa ion (AFL; F ance), Aus ian Limnological Socie y (SIL-
Aus ia), as well as he Leibniz-Ins i u e o F eshwa e Ecology and Inland Fishe ies o
addi ional unds. Addi ional unding was awa ded o J.P.C.-R. by a Juan de la Cie a
pos doc o al g an om he Spanish Go e nmen (FJC2018-037791-I), o A.P.P. by a Ph.
D. g an om he Fundação pa a a Ciência e Tecnologia (SFRH/BD/115030/2016), o
B.C.D. by he Ma ine Ins i u e’s Cullen Ph.D. ellowship (G an No. CF/15/05), o N.C.
by he Eu opean Union’s Ho izon 2020 esea ch and inno a ion p og am unde he
Ma ie Sklodowska-Cu ie g an ag eemen (No. 839709), o J.M. by FCT (Po uguese
Science Founda ion) h ough a Ph.D. g an (SFRH/BD/131924/2017), o J.P. by he DSI/
NRF Resea ch Chai in Inland Fishe ies and F eshwa e Ecology, o A.F. by he Juan de la
Cie a pos doc o al g an om he Spanish Go e nmen (FJCI-2017–33171), and o
C.M.-L. by he F ench Na ional Agency o Wa e and Aqua ic En i onmen s (ONEMA,
Ac ion 13, “Colma age, échanges nappe- i iè e e p ocessus biogéochimiques”). We
acknowledge Luigi Naselli-Flo es and An onio Camacho o hei encou agemen and
suppo du ing he p ojec . We also hank Da id Bas iken, Ing id Sundg en, and Thanh
Duc Nguyen o he in oduc ion o he logge and chambe cons uc ion and ad ice o
measu emen s o CO
2
fluxes wi h he chambe , Vincen Fugè e o his help in se ing up
he linea mixed-e ec models, and Vik o Rosenbe g o c ea ing he map. Fu he mo e,
we a e e y hank ul o Ra ael Ma cé and Paul del Gio gio o hei hough ul commen s
on he manusc ip and we hank h ee anonymous e iewe s o cons uc i e inpu s ha
imp o ed he manusc ip . Open access unding p o ided by Uni e si y o Vienna.
Au ho con ibu ions
K.A. and P.B. concei ed he s udy design, coo dina ed he p ojec and con ibu ed
equally o his wo k; all au ho s collec ed and analyzed he field da a and K.A. and P.B.
ga he ed and pe o med he quali y check o all da a; K.A., P.B., and J.P.C.-R. co-w o e
he pape wi h he help o M.K., G.H.N., and N.C. All au ho s (K.A., J.P.C.-R., T.F., A.P.,
S.C.-F., D.S., A.C.N., Al.D., A.P.P., B.C.D., N.S., C.G.R., G.H.N., X.T., V.E., L.B.-F., T.B.,
J.A., An.D., G.B., S.F., N.C., E.d.E., F.P., J.-R.M., J.M., D.F., C.N., M.C., M.N., L.L., C.R.
G.-Q., F.R., N.P., J.L.J.L., J.P., M.K., A.F., S.H.O., C.M.-L., A.B., J.A.F., P.J.G., L.A.K.,
M.R., P.B.) commen ed on he manusc ip .
Compe ing in e es s
The au ho s decla e no compe ing in e es s.
Addi ional in o ma ion
Supplemen a y in o ma ion The online e sion con ains supplemen a y ma e ial
a ailable a h ps://doi.o g/10.1038/s43247-021-00192-w.
Co espondence and eques s o ma e ials should be add essed o K.A.
Pee e iew in o ma ion Communica ions Ea h & En i onmen hanks he anonymous
e iewe s o hei con ibu ion o he pee e iew o his wo k. P ima y Handling
Edi o s: Joshua Dean and Joe Aslin.
Rep in s and pe mission in o ma ion is a ailable a h p://www.na u e.com/ ep in s
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Open Access This a icle is licensed unde a C ea i e Commons
A ibu ion 4.0 In e na ional License, which pe mi s use, sha ing,
adap a ion, dis ibu ion and ep oduc ion in any medium o o ma , as long as you gi e
app op ia e c edi o he o iginal au ho (s) and he sou ce, p o ide a link o he C ea i e
Commons license, and indica e i changes we e made. The images o o he hi d pa y
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1
Limnology/Depa men o Ecology and Gene ics, Uppsala Uni e si y, Uppsala, Sweden.
2
Wasse Clus e Lunz –Biologische S a ion, Lunz am See,
Aus ia.
3
Depa men o Func ional and E olu iona y Ecology, Uni e si y o Vienna, Vienna, Aus ia.
4
Ca alan Ins i u e o Wa e Resea ch
(ICRA), Gi ona, Spain.
5
Uni e si y o Gi ona (UdG), Gi ona, Spain.
6
Flu ial Ecosys em Ecology, Depa men o Ecology, Uni e si y o Innsb uck,
Innsb uck, Aus ia.
7
INRAE, UR Ri e ly, Cen e de Lyon-Villeu banne, Villeu banne, Cedex, F ance.
8
Depa men o Li e and En i onmen al
Sciences, Bou nemou h Uni e si y, Poole, UK.
9
Depa men o Sciences and Technological Inno a ion, Uni e si y o Piemon e O ien ale,
Alessand ia, I aly.
10
ALPSTREAM –Alpine S eam Resea ch Cen e , Os ana, I aly.
11
Resea ch Cen e in Biodi e si y and Gene ic Resou ces
(CIBIO-InBIO), Uni e si y o Po o, Vila do Conde, Po ugal.
12
Facul y o Sciences, Uni e si y o Po o, Po o, Po ugal.
13
Cen e o F eshwa e and
En i onmen al S udies, Dundalk Ins i u e o Technology, Dundalk, Co Lou h, I eland.
14
Na ional Museum o Na u al His o y, Bulga ian Academy o
Sciences, Sofia, Bulga ia.
15
Ri e and Conse a ion Resea ch, Depa men o Ecology, Uni e si y o Innsb uck, Innsb uck, Aus ia.
16
Depa men o
Aqua ic Ecosys ems, Ins i u e o Biodi e si y and Ecosys em Resea ch, Bulga ian Academy o Sciences, Sofia, Bulga ia.
17
Depa men o Aqua ic
Sciences and Assessmen , Swedish Uni e si y o Ag icul u al Sciences, Uppsala, Sweden.
18
Depa men o Ecology and En i onmen al Science,
Umeå Uni e si y, Umeå, Sweden.
19
Depa men o Li e Sciences and Sys ems Biology, Uni e si y o Tu in, Tu in, I aly.
20
Ma ine Ins i u e, Fu nace,
Newpo , Co Mayo, I eland.
21
Depa men o E olu iona y Biology, Ecology and En i onmen al Sciences, Facul y o Biology, Uni e si y o
Ba celona (UB), Ba celona, Spain.
22
Cen e o Ecology, E olu ion and En i onmen al Changes (cE3c), Faculdade de Ciências, Uni e sidade de
Lisboa, Lisboa, Po ugal.
23
Ins i u e o En i onmen al Sciences, Uni e si y o Koblenz-Landau, Landau, Ge many.
24
Ins i u e o Mic obiology,
Uni e si y o Innsb uck, Innsb uck, Aus ia.
25
Expe imen al Limnology, Leibniz-Ins i u e o F eshwa e Ecology and Inland Fishe ies (IGB), S echlin,
Ge many.
26
Ecohyd ology, Leibniz-Ins i u e o F eshwa e Ecology and Inland Fishe ies (IGB), Be lin, Ge many.
27
Cen e o Ad anced S udies o
Blanes, Spanish Na ional Resea ch Council, Blanes, Spain.
28
Ins i u e o Geog aphy and Geoecology, Ka ls uhe Ins i u e o Technology, Ka ls uhe,
Ge many.
29
Sou h A ican Ins i u e o Aqua ic Biodi e si y, Makhanda, Sou h A ica.
30
Depa men o Ecology and En i onmen al Sciences,
Palacký Uni e si y Olomouc, Olomouc, Czech Republic.
31
En i onmen al Resea ch Ins i u e, Uni e si y o Highlands and Islands (UHI), Thu so,
Sco land, UK.
32
Depa men o Gene al and Applied Hyd obiology, Sofia Uni e si y “S . Klimen Oh idski”,Sofia, Bulga ia.
33
Chemical Analy ics
and Biogeochemis y, Leibniz-Ins i u e o F eshwa e Ecology and Inland Fishe ies, Be lin, Ge many.
34
P esen add ess: Depa men o Biology,
Aa hus Uni e si y, Aa hus C, Denma k.
35
P esen add ess: Ins i u e o Global Heal h, Facul y o Medicine, Uni e si y o Gene a, Campus Bio ech,
Gene a, Swi ze land.
36
P esen add ess: Cen e o En i onmen , Fishe ies and Aquacul u e Science (Ce as), Lowes o , Su olk, UK.
37
P esen
add ess: Depa men o Bioscience, Aa hus Uni e si y, Silkebo g, Denma k.
38
P esen add ess: No wegian Ins i u e o Wa e Resea ch, Oslo,
No way.
39
P esen add ess: Labo a oi e des Sciences du Clima e de l’En i onnemen (LSCE), CEA, CNRS, UVSQ, Gi -Su -Y e e, F ance.
40
P esen add ess: Uni ed S a es Geological Su ey, Boulde , CO, USA.
41
P esen add ess: En i onmen al A chaeology Lab, Depa men o
His o ical, Philosophical and Religious s udies, Umeå Uni e si y, Umeå, Sweden.
42
P esen add ess: Depa men o Fo es Ecology and
Managemen , Swedish Uni e si y o Ag icul u al Sciences, Umeå, Sweden.
43
P esen add ess: Global Change Resea ch Ins i u e o he Czech
Academy o Sciences, B no, Czech Republic.
44
P esen add ess: G oupe de Reche che In e uni e si ai e en Limnologie, Dépa emen des Sciences
Biologiques, Uni e si é du Québec à Mon éal, Mon éal, Canada. ✉email: [email p o ec ed]
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