1
LENA RIVER DELTA SIBERIA COLORED DISSOLVED ORGANIC MATTER (CDOM) CHARACTERIZATION BY ABSORPTION AND FLUORESCENCE SPECTRA Funding Helmholtz Association (Germany), CAPES (Brazil), DAAD (Germany), The Total Foundation, POLMAR (AWI-Germany) Aknowledgments The authors thank to Dr. Colin Stedmon (DTU-Aqua, Denmark) for the colaboration for the PARAFAC analysis, Sonja Wiegmann (AWI), Dr. Elena Torrecilla (ICM, Spain) BREMERHAVEN Bussestraße 24 27570 Bremerhaven Telefon 0471 4831-1785 www.awi.de Ebro Delta ALFACS BAY LENA DELTA Arctic Ocean Laptev Sea Mediteranean Sea INTRODUCTION MATERIAL AND METHODS EBRO RIVER DELTA SPAIN Expeditions/Projects: Lena (L, Sep/13) and Phytoscope (P, Jun/13 and Mar/14) Sensors: CTD cats, TriOS/RAMSES Water samples: CDOM/FDOM, Particulate matter absorption, phytoplankton Analysis: EEM/PARAFAC analysis for DOM (Stedmon & Bro, 2008; Murphy et al., 2013) HPLC/CHEMTAX - phytoplankton pigments (Barlow 2007; Mackey et al, 1996) R RS (P), vertical attenuation coefficients (Stramski et al., 2008) Algal and non-algal particulate absorption (Ferrari & Tassan, 1999) Salinity a 350 Salinity a 350 Hydrography and CDOM absorption @ 350nm EEM-PARAFAC results Hydrography and CDOM absorption @ 350nm EEM-PARAFAC results Particulate matter absorption Contact [email protected] Rafael Gonçalves-Araujo 1 , M. Ramírez-Pérez 2 , A. Kraberg 3 , J. Piera 2 , A. Bracher 1,4 1 Alfred Wegener Institute (AWI), Climate Sciences, PHYTOOPTICS Group Bremerhaven Germany 2 Institute of Marine Sciences, Consejo Superior de Investigaciones Científicas, Barcelona Spain 3 Alfred Wgener Institute (AWI), Biologische Anstalt Helgoland, Helgoland Germany 4 University of Bremen, Institute of Environmental Physics (IUP), Bremen Germany a 350 Components vs a 350 Salinity 2083 One of the largests rivers in the world ~20% total fresh water in the Arctic Ocean (Cauwet & Sidorov, 1996) Greatest discharge of organic matter in the Arctic Stedmon et al. (2011) Under climate changing pressure (Yang et al., 2002) Permafrost thaw river discharge (Lyon & Destouni, 2010) First attenuation depth (Heim et al., 2014) Dissolved organic matter (DOM) Chromophoric DOM (CDOM) Fluorescent DOM (FDOM) Important component of the Carbon cycle considerable riverine input Important factor on controlling ocean productivity absorbs light mainly in UV and Visible Can be detected by ocean color remote sensing Amount and composition can be detected by applying optical analysis Many processes can lead to a variability of DOM in the ocean OBJECTIVE - To asses the dynamics of DOM through its amount and composition determined by using optical techniques One of the most important rivers in the Iberian Peninsula 2 nd largest in Spain The delta region is important for rice and mussel cultures (Ramón et al., 2005) HAB and phycotoxins (Fernández-Tejedor et al., 2008) shellfish harvesting closures Em. (nm) Ex. (nm) Ex. (nm) Ex. (nm) Ex. (nm) Ex. (nm) Ex. (nm) Fmax (nm -1 ) Humic-like Mostly removed Low salinity Walker et al. 2013 Humic-like Allochthonous Mostly removed Low salinity Walker et al. 2013 Marine humic-like Autochthonous Mostly removed High salinity Humic-like Allochthonous Mostly removed Equally distributed Humic-like Mostly released High salinity Walker et al. 2013 Chari et al., 2013 Protein-like Autochthonous Mostly released High salinity Walker et al. 2013 Chari et al., 2013 Outlook - Look at the DOC and phytoplankton data - Humification/Aromaticiy indices - Removal processes: photodegradation, floculation and bacterial degradation - Release processes: microbial production, river discharge - DOM discharge into the Arctic Ocean and residence time Conclusions - Optical spectra good for DOM characterisation - DOM variability modulated by hydrography - DOM components presented diverse behaviors - Different processes over DOM dynamics CDOM distribution modulated by hydrography Non-conservative behavior in relation to salinity REMOVAL OF CDOM Up to 55% of removal a 350 extrapolation to fresh and marine waters in agreement with literature - No signifcant differences between Summer and Winter for salinity - Temperature and a 350 were signifcant different between the campaigns A 350 inversely related to S 275-295 Components 1 & 3 more contributed to the total DOM Humic-like Common component Higher in Summer Tryptophan-like Autochthonous Higher in Summer Tyrosine-like Autochthonous No significant diff. Humic-like Allochthonous Higher in Summer Conclusions - Significant differences were found between Summer/Winter - Tyrosine-like component did not vary between campaigns - Higher a det in Winter probably resuspension - Higher a ph in Summer higher light/nutrient input Outlook - Determine phytoplankton composition by applying CHEMTAX - Analise the R RS and attenuation coefficients - Relate light attenuation with water components - Look at the influence of phytoplankton on DOM release - Verify the varibiliaty between Summer and Winter a det(443) = 0.165m -1 p < 0.05 a det(443) = 0.193m -1 p < 0.05 a ph(443) = 0.240m -1 p < 0.01 a ph(443) = 0.330m -1 p < 0.01 Fmax (nm -1 ) Normalised Fmax (nm -1 )

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Page 1: COLORED DISSOLVED ORGANIC MATTER (CDOM ...LENA RIVER DELTA – SIBERIA COLORED DISSOLVED ORGANIC MATTER (CDOM) CHARACTERIZATION BY ABSORPTION AND FLUORESCENCE SPECTRA Funding …

LENA RIVER DELTA – SIBERIA

COLORED DISSOLVED ORGANIC MATTER (CDOM) CHARACTERIZATION

BY ABSORPTION AND FLUORESCENCE SPECTRA

Funding

Helmholtz Association (Germany), CAPES (Brazil), DAAD (Germany), The Total Foundation, POLMAR (AWI-Germany)

Aknowledgments

The authors thank to Dr. Colin Stedmon (DTU-Aqua, Denmark) for the colaboration for the PARAFAC analysis, Sonja Wiegmann (AWI), Dr. Elena Torrecilla (ICM, Spain)

BREMERHAVEN

Bussestraße 24

27570 Bremerhaven

Telefon 0471 4831-1785

www.awi.de

Ebro Delta

ALFACS BAY LENA DELTA

Arctic Ocean

Laptev Sea

Mediteranean Sea

INTRODUCTION

MATERIAL AND METHODS

EBRO RIVER DELTA – SPAIN

● Expeditions/Projects: Lena (L, Sep/13) and Phytoscope (P, Jun/13 and Mar/14)

● Sensors: CTD cats, TriOS/RAMSES

● Water samples: CDOM/FDOM, Particulate matter absorption, phytoplankton

● Analysis: EEM/PARAFAC analysis for DOM (Stedmon & Bro, 2008; Murphy et al., 2013)

HPLC/CHEMTAX - phytoplankton pigments (Barlow 2007; Mackey et al, 1996)

RRS (P), vertical attenuation coefficients (Stramski et al., 2008)

Algal and non-algal particulate absorption (Ferrari & Tassan, 1999)

Salinity

a350

Salinity

a350

• Hydrography and CDOM absorption @ 350nm

• EEM-PARAFAC results

• Hydrography and CDOM absorption @ 350nm

• EEM-PARAFAC results

• Particulate matter absorption

Contact [email protected]

Rafael Gonçalves-Araujo1, M. Ramírez-Pérez2, A. Kraberg3, J. Piera2, A. Bracher1,4

1Alfred Wegener Institute (AWI), Climate Sciences, PHYTOOPTICS Group Bremerhaven – Germany 2Institute of Marine Sciences, Consejo Superior de Investigaciones Científicas, Barcelona – Spain 3Alfred Wgener Institute (AWI), Biologische Anstalt Helgoland, Helgoland – Germany 4University of Bremen, Institute of Environmental Physics (IUP), Bremen – Germany

a350

Components vs a350

Salinity

2083

● One of the largests rivers in the world

~20% total fresh water in the Arctic Ocean (Cauwet & Sidorov, 1996)

● Greatest discharge of organic matter in the Arctic

Stedmon et al. (2011)

● Under climate changing pressure (Yang et al., 2002)

Permafrost thaw river discharge (Lyon & Destouni, 2010) First attenuation depth (Heim et al., 2014)

● Dissolved organic matter (DOM) – Chromophoric DOM (CDOM) – Fluorescent DOM (FDOM)

● Important component of the Carbon cycle – considerable riverine input

● Important factor on controlling ocean productivity absorbs light mainly in UV and Visible

● Can be detected by ocean color remote sensing

● Amount and composition can be detected by applying optical analysis

● Many processes can lead to a variability of DOM in the ocean OBJECTIVE

- To asses the dynamics of DOM

through its amount and composition

determined by using optical techniques

● One of the most important rivers in the Iberian Peninsula – 2nd largest in Spain

● The delta region is important for rice and mussel cultures (Ramón et al., 2005)

● HAB and phycotoxins (Fernández-Tejedor et al., 2008) shellfish harvesting closures

Em. (

nm

)

Ex. (nm) Ex. (nm) Ex. (nm) Ex. (nm) Ex. (nm) Ex. (nm)

Fmax

(n

m-1

)

Humic-like Mostly removed

Low salinity Walker et al. 2013

Humic-like Allochthonous

Mostly removed Low salinity

Walker et al. 2013

Marine humic-like Autochthonous Mostly removed

High salinity

Humic-like Allochthonous

Mostly removed Equally distributed

Humic-like Mostly released

High salinity Walker et al. 2013 Chari et al., 2013

Protein-like Autochthonous Mostly released

High salinity Walker et al. 2013 Chari et al., 2013

● Outlook - Look at the DOC and phytoplankton data

- Humification/Aromaticiy indices - Removal processes: photodegradation, floculation and bacterial degradation - Release processes: microbial production, river discharge - DOM discharge into the Arctic Ocean and residence time

● Conclusions - Optical spectra good for DOM characterisation

- DOM variability modulated by hydrography

- DOM components presented diverse behaviors

- Different processes over DOM dynamics

CDOM distribution modulated by hydrography

Non-conservative behavior in relation to salinity REMOVAL OF CDOM Up to 55% of removal

a350 extrapolation to fresh and marine waters in agreement with literature - No signifcant differences between Summer and Winter for salinity

- Temperature and a350 were signifcant different between the campaigns A350 inversely related

to S275-295

Components 1 & 3 more contributed to the total DOM

Humic-like Common component

Higher in Summer

Tryptophan-like Autochthonous

Higher in Summer

Tyrosine-like Autochthonous

No significant diff.

Humic-like Allochthonous

Higher in Summer

● Conclusions

- Significant differences were found between Summer/Winter

- Tyrosine-like component did not vary between campaigns

- Higher adet in Winter probably resuspension

- Higher aph in Summer higher light/nutrient input

● Outlook - Determine phytoplankton composition by applying CHEMTAX

- Analise the RRS and attenuation coefficients

- Relate light attenuation with water components

- Look at the influence of phytoplankton on DOM release

- Verify the varibiliaty between Summer and Winter

adet(443) = 0.165m-1

p < 0.05

adet(443) = 0.193m-1

p < 0.05

aph(443) = 0.240m-1

p < 0.01

aph(443) = 0.330m-1

p < 0.01

Fmax

(n

m-1

) N

orm

alis

ed F

max

(n

m-1

)