Correspondence: Felix Mark, Hans Pörtner | Integrative Ecophysiology | Alfred Wegener Institute for Polar & Marine Research, 27570 Bremerhaven, Germany | e: fmark@awi.de, hans.poertner@awi.de | p: +49-471-4831-1015, -1307
The concept of oxygen and capacity limitation of thermal tolerance (OCLT) provides a matrix integrating the synergistic effects of environmental stressors including ocean acidification. The thermal window is narrowed through CO
2specific effects on molecular to whole organism functions. Available evidence suggests that the OCLT concept closely defines the sensitivity and response of individuals to climate change at ecosystem level. It also provides causality and quantifies the levels and changes of organism performance and resistance as a reason for changes in species interactions
1. An understanding of ecosystem-level processes results as needed to achieve more realistic estimates of species and ecosystem sensitivities to environmental change.
Which physiological mechanisms explain the different sensitivities and synergistic effects observed?
References: 1) Pörtner (2010) J Exp Biol 213:881-893 2) Walther et al. (2009) Biogeosciences 6:2207-2215 3) Walther et al. (2010) Mar Ecol Prog Ser 417:159-170 4) Deigweiher et al. (2008) Am J Physiol 295:R1660-1670
5. Ecosystem effects involve multiple stressors:
General Model
Genetic level: mRNA expression (x-fold) of gill Na+/HCO3- cotransporter (NBC1) is reduced in long-term warm acclimated Antarctic eelpout P. brachycephalum. Expression was normalized to β-actin and given relative to the expression of the respective control group animals.
CO2 may reduce the capacity of the warm acclimation response in Antarctic fish gills and thereby contribute to an earlier onset of thermal stress.
Acclimation condition
0°C 5°C 5°C + CO2
NBC1 expression (x-fold)
0.0 0.2 0.4 0.6 0.8 1.0 1.2
* **
* * *
#
Mitochondrial level: Mitochondrial capacities that generally are in excess of whole organism functional capacities and energy turnover are thermally less responsive under elevated PCO2 in Antarctic notothenioids.
At thermal extremes, mitochondria may not display sufficient capacity to meet whole organism energy demand causing an earlier onset of thermal stress.
7. Synergistic effects: Mechanisms underneath
Q10: 3.2 Q10: 2.1 Q10: 2.1 Q10: 1.9
ComplexII state III respiration
0 6 12 0 6 12 0 6 12 0 6 12 0
1 2 3 4 5 6 7
8 #
assay temperature [°C]
[nmol O 2*min-1 *mg-1 ]
0°C 0°C, 0.2kPa 7°C 7°C, 0.2kPa
Pachycara brachycephalum
Notothenia rossii
Strobel et al., in prep.
Sun et al., in prep.
6. Confirmation of general model
Whole organism level: CO2 sensitivity is temperature dependent, and, vice versa, temperature sensitivity is CO2 dependent.
The thermal window of the spider crab Hyas araneus is progressively narrowed by elevated CO2 levels, indicated by the shift in upper critical temperature (Tc) to lower values2.
Hyas araneus Walther et al., 2009
Working model for acid-base regulation under hypercapnia in the gills of the marine teleost Zoarces viviparus4. Red circles: gene expression during short-term hypercapnia (24 to 96 h), green circles: long-term response (6wks). mRNA levels were found to be up-regulated (+), down-regulated (-) or unchanged (=). HA: H+-ATPase, NHE1/2/3: Na+/H+-exchanger isoforms, CA: Carbonic anhydrase, AE1: Cl-/HCO3- -exchanger, NKA:
Na+/K+-ATPase, NBC1: Na+/HCO3— co-transporter, NKCC: Na+/K+/2Cl— co-transporter. Open arrows: changes in substrate concentrations.
environment fish gill epithelium blood
CO2
NBC1 HCO3
NHE2/3
H+ Na+
2 K+ K+
H2O
HCO3 H+
CA +
Cl- AE1
HCO3
Cl- Na+
+
NKA ATP
ATP
NKCC
Na+ H+
Na+ K+ 2 Cl- Na+
3 Na+
Na+
NHE1
CO2
Cl--channel HA
K+channel Na+channel
Na+
-
+
+
=
=
+ -
-
+ +
+
-
+
Net H+ extrusion H+
-
-
-
4. Specific effects:
Gene expression in fish gills
STIRRER
TEMPERATURE CONTROLLED CHAMBER
3. Specific effects:
Energy budget of fish gills
V-type ATPase (Bafilomycin)
Cl-/ HCO3- exchanger
(DIDS)
Na+/ K+ ATPase (Ouabain) Na+/ H+
exchanger (EIPA)
With full compensation of acid-base status, some ion transporters in perfused cod gills display enhanced turnover rates indicating elevated energy demand and a shift in gill energy budget elicited by changes in PCO2.
control
inside (perfusate)outside (seawater)
Gadus morhua
Schaum et al., in prep.
7,4 7,5 7,6 7,7
7,3 7,8
extracellular [HCO 3- ] (mM)
0 2 4 6 8 10 12 14
2,26 1,86 1,60 1,33 1,07
0,80
0,53
0,27 0,13 PCO2 (kPa)
βNB = 8.95 mmol/pH/l
pH
PCO2 (kPa) 0.04
0.2 0°C 7°C
Bivalves like the Greenland Smoothcockle (Serripes groenlandicus) only passively regulate extracellular pH regardless of temperature.
2. Specific effects: Acid-base Regulation in Polar Organisms
0,0 0,5 1,0 1,5 2,0 2,5
7 7,1 7,2 7,3 7,4 7,5 7,6 7,7 7,8 7,9 8 8,1
0,0 0,5 1,0 1,5 2,0 2,5
7,0 7,1 7,2 7,3 7,4 7,5 7,6 7,7 7,8 7,9 8,0 8,1
2,5 2,0 1,5 1,0 0,5 0,0
2,5 2,0 1,5 1,0 0,5 0,0
2,5 2,0 1,5 1,0 0,5
0,07,0 7,2 7,4 7,6 7,8 8,0
extracellular pH CH ralullecartxeO 3- ]Mm[
~4°C
~1°C
~7°C
~380 ppm
~750 ppm
~3000 ppm ~1120 ppm
CH ralullecartxeO 3- ]Mm[ CH ralullecartxeO 3- ]Mm[
βNB=0.4 mmol/pH/l
PCO 2(sea water):
1330 660
2000 2660
4000 5330
6670 :extracellular
PCO2(ppm)
1330 660
2000 2660
4000 5330
6670
1330 660
2000 2660
4000 5330
6670
:extracellular PCO2(ppm)
:extracellular PCO2(ppm)
βNB=0.4 mmol/pH/l βNB=0.4 mmol/pH/l
Stark et al., in prep.
Strobel et al., in prep.
Serripes groenlandicus
Notothenia rossii
Antarctic fish (Notothenia rossii) show a compensation of blood pH by active HCO3- uptake at low temperatures and even overcompensation at warm temperatures.
Organisms from polar areas are exposed to the largest changes in PCO2 and may be most sensitive due to low capacities of physiological functions and low metabolic rates.
Hyas araneus larvae
In Megalopae and post larvae of the spider crab Hyas araneus from Arctic and temperate regions, hypercapnia leads to developmental delay and enhanced mortality, illustrating the high sensitivity of early life stages3.
1. Whole Organism Synergistic Effects (e.g. crab larvae)
0 20 40 60 80 100 120 140 0
20 40 60 80
100 9°C
Survival (%)
0 10 20 30 40 50 60 70
0 20 40 60 80
100 15°C
0 20 40 60 80 100 120 140 0
20 40 60 80
100 9°C
Developmental time (d)
Survival (%)
0 10 20 30 40 50 60 70
0 20 40 60 80 100
Normocapnia 710 ppm 3000 ppm
15°C
Normocapnia 710 ppm 3000 ppm
Developmental time (d)
Helgoland (south)
Svalbard (north)
Megalopa Crab I
(source: Schiffer/Harms)
Walther et al., 2010