Conley Supporting Information

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Supporting Information

Hypoxia is increasing in the coastal zone of the Baltic Sea Daniel J. Conley1, Jacob Carstensen2, Juris Aigars3, Philip Axe4, Erik Bonsdorff5, Tatjana Eremina6, Britt-Marie Haahti5, Christoph Humborg7,8, Per Jonsson8, Jonne Kotta9, Christer Lännegren10, Ulf Larsson11, Alexey Maximov12, Miguel Rodriguez Medina7, Elzbieta Lysiak-Pastuszak13, Nijolė Remeikaitė-Nikienė14, Jakob Walve11, Sunhild Wilhelms15, and Lovisa Zillén1 1

Department of Earth and Ecosystem Sciences, Lund University, SE-223 62 Lund, Sweden

2

National Environmental Research Institute, Aarhus University, DK-4000 Roskilde, Denmark

3

Latvian Institute of Aquatic Ecology, LV-1007 Riga, Latvia

4

Swedish Meteorological & Hydrological Institute, SE-426 71 Västra Frölunda, Sweden

5

Department of Biosciences, Environmental and Marine Biology, Åbo Akademi University, BioCity , FI-20520 Turku/Åbo, Finland 6

Russian State Hydrometeorological University, 195196 St. Petersburg, Russia

7

Baltic Nest Institute, Stockholm University, SE-106 91 Stockholm, Sweden

8

Department of Applied Environmental Science, Stockholm University, SE-11418 Sweden

9

Estonian Marine Institute, University of Tartu, 12618 Tallinn, Estonia

10

Stockholm Vatten, SE-106 36 Stockholm, Sweden

11

Department of Systems Ecology, Stockholm University, SE-106 91 Stockholm, Sweden

12

Zoological Institute, Russian Academy of Science, 199034 St. Petersburg, Russia

13

Institute of Meteorology and Water, Management Maritime Branch, 81-342 Gdynia, Poland

14

Environmental Protection Agency, Department of Marine Research, LT-91149 Klaipeda, Lithuania 15

Bundesamt für Seeschifffahrt und Hydrographie, D-20359 Hamburg, Germany

S1

Table S1. Data sources for the analysis of hypoxia in the coastal zone of the Baltic Sea. All known data sources for oxygen concentrations in the coastal zone of the Baltic Sea were compiled. The list of data providers are in Table S1. Most of the data assembled are archived in the Baltic Environmental Database (BED) (http://nest.su.se/models/bed.htm) of the Baltic Nest Institute, Stockholm University. However, data from Russia and from the Himmerfjärden, Ulf Larsson, Systems Ecology, Stockholm University are not archived in the BED database. Access to the data can be obtained from the original data holders identified in Table S1. The location of monitoring data used in this study were partitioned into different regions largely following the division of HELCOM – The Helsinki Commission: Baltic Marine Environmental Protection Commission (Figure S1). Country

Data Host

Provider

Access Level

Denmark

National Environmental Research

Jacob Carstensen

Public access

Institute Estonia

Estonian Marine Institute

Jonne Kotta

Restricted

Finland

Finnish Environmental Institute

Jouko Rissanen

Public access

Germany

Bundesamt fuer Seeschifffahrt und

Sunhild Wilhelms

Public access

Hydrographie (BSH) Latvia

Latvian Institute of Aquatic Ecology

Juris Aigars

Restricted

Lithuania

Environmental Protection Agency

Nijolė Remeikaitė-Nikienė

Restricted

Poland

Chief Inspectorate for Environmental

Elzbieta Lysiak-Pastuszak

Restricted

Alexey Maximov

Restricted

Protection Russia

Russian Academy of Science

Sweden

Swedish Meteorological & Hydrological Philip Axe

Public access

Institute Sweden

Stockholm University

Ulf Larsson

S2

Restricted

Sweden

Stockholm Vatten

Christer Lännergren

S3

Public access

Table S2. Identified seasonal windows for calculating trends in oxygen concentrations (Figure 4, manuscript). The seasonal windows cover the summer and autumn months when the seasonal trend in bottom oxygen becomes decoupled from the seasonal trends in the surface water. Bottom water oxygen concentrations reached their annual minimum at different times of the year and for different amounts of time partly depending upon their geographical location. Therefore, seasonal windows where hypoxia occurs were calculated using the mean monthly profiles. Region

Jan

Feb Mar Apr May Jun

Bothnian Bay The Quark Bothnian Sea Stockholm Archipelago Finnish Archipelago Gulf of Finland Gulf of Riga Western Gotland basin Eastern Gotland basin Southern Baltic Proper Belt Seas The Sound The Kattegat Limfjord

S4

Jul

Aug Sep Oct

Nov Dec

Figure S1. Location of monitoring data used in the study, partitioned into different regions, largely following the regional division from HELCOM.

S5

Frequency of hypoxic profiles

16.0%

12.0%

8.0%

4.0%

Q ua Bo rk th nia n St Se oc a kh ol m Ar ch Fi nn . ish Ar G ch ul fo . fF in la nd G ul f of W Ri G ga ot la nd E ba G sin ot la nd ba S sin Ba ltic Pr op er Be lt S ea s Th e So un Th d e Ka tte ga t Li m fjo rd

Th e

Bo th nia n

Ba y

0.0%

Figure S2. The number of hypoxic profiles relative to the total number of profiles for the different regions of the Baltic Sea over the entire period (1955-2009).

S6

2

Surface Bottom Difference

1 0

3

-1

0

-2 F

M

A

M

J

J

A

S

O

N

-1

9

3

Surface Bottom

6

2

Difference

3

1

0

D

0 J

F

M

A

M

J

Months 15

5

Surface Bottom

2

Difference

1

3

-1

3

-1 Concentration (mg l )

4

12

Difference (mg l )

-1

Concentration (mg l )

Bothnian Sea

6

0

0

-1 J

F

M

A

M

J

J

A

S

O

N

5 9

4 3

6

1 Surface Bottom Difference

0

Concentration (mg l-1)

2

6

M

A

M

-2 J

A

S

O

N

Surface Bottom

0

Difference M

J

J

A

S

-1 O

N

Concentration (mg l-1)

1

Difference (mg l-1)

Concentration (mg l-1)

2 6

A

D

5

9

3 Surface Bottom Difference

6

2

3

1

0 F

M

A

15

5

3

M

N

4

J

9

F

O

0

4

J

S

M

J

J

A

S

O

N

D

Months

12

0

A

12

D

Gulf of Riga

3

J

Gulf of Finland

Months 15

J

-1

0 J

1 0

F

15

Difference (mg l-1)

Concentration (mg l-1)

3

M

2

Surface Bottom Difference

3

6

4

A

7 6

J

7

9

M

D

0

5

F

N

Months

12

J

O

12

D

Finnish Archipelago

3

S

Stockholm Archipelago

Months 15

A

Months

15

9

J

Difference (mg l-1)

J

4

Difference (mg l-1)

6

12

12

4

9

3

6

2 Surface Bottom Difference

3

0

D

J

Months

F

M

A

M

J

J

Months

S7

5

W Gotland basin

A

S

1

0 O

N

D

Difference (mg l-1)

9

-1

3

Concentration (mg l )

4

12

5

The Quark -1 Difference (mg l )

-1 Concentration (mg l )

15

5

Bothnian Bay

Difference (mg l )

15

15

2 Surface Bottom

1

Difference

0

0

-1 J

F

M

A

M

J

J

A

S

O

N

4 -1

9

3 Surface Bottom Difference

6

2

3

1

0

D

0 J

F

M

A

M

Months

2 Surface Bottom Difference M

A

1

-1

6

Concentration (mg l )

3

-1

9

Difference (mg l )

Concentration (mg l-1)

4

F

J

J

A

S

O

N

9

3

6

2 Surface

3

1

Bottom Difference J

F

M

A

0 M

15

12

4

12

9

3

Surface Bottom Difference M

A

1 0 M

J

J

A

S

O

N

-1 Concentration (mg l )

-1

2

F

J

A

S

O

N

D

5

Limfjord Difference (mg l )

-1

Concentration (mg l )

6

J

J

Months 5

0

D

4

D

The Kattegat

3

N

12

Months 15

O

5

0

0 M

S

The Sound

12

J

A

15

5

Belt Seas

0

J

Months

15

3

J

-1 Difference (mg l )

3

12

4 3

9 Surface Bottom Difference

6

2 1

3

0

0

D

-1 J

Months

Difference (mg l-1)

6

-1 Concentration (mg l )

3 9

Difference (mg l-1)

4

12

5

S Baltic Proper

Difference (mg l )

5

E Gotland basin

-1

Concentration (mg l )

15

F

M

A

M

J

J

A

S

O

N

D

Months

Figure S3. Seasonal variation in surface and bottom water oxygen concentration as well as their difference for the 14 regions delimited in Figure S1. Bottom oxygen means were calculated only when the density difference between surface and bottom was above 0.5, i.e. indicative of a stratified water column. Seasonal patterns in water column oxygen concentrations were observed across the entire Baltic Sea coastal zone with August and September generally being the peak months for

S8

hypoxia in all regions. Further south in the Baltic Sea coastal zone hypoxia also occurred in October and in some cases into November in the Sound and the Kattegat coastal regions. The periods of time, e.g. the seasonal window when hypoxia appears, used for calculating trends in oxygen concentrations, are in Table S2.

S9

0.60%

0.60%

The Quark

0.50%

Frequency of hypoxic profiles

Frequency of hypoxic profiles

Bothnian Bay

0.40% 0.30% 0.20% 0.10%

0.50% 0.40% 0.30% 0.20% 0.10% N/A

0.00% 0-5

0-5

5-10 10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50 >50

>50

50%

Stockholm Archipelago

Bothnian Sea 5.0%

Frequency of hypoxic profiles

Frequency of hypoxic profiles

N/A

Depth (m)

6.0%

4.0% 3.0% 2.0% 1.0%

40%

30%

20%

10%

0%

0.0% 0-5

5-10 10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50

>50

0-5

5-10

Depth (m)

10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50 Depth (m)

>50

15%

15%

Gulf of Finland Frequency of hypoxic profiles

Finnish Archipelago Frequency of hypoxic profiles

N/A

5-10 10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50

Depth (m)

10%

5%

10%

5%

0%

0% 0-5

5-10

10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50

>50

0-5

5-10

Depth (m) 2.0%

10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50 Depth (m)

>50

25%

Western Gotland basin Frequency of hypoxic profiles

Gulf of Riga Frequency of hypoxic profiles

N/A

0.00%

1.5%

1.0%

0.5%

N/A

N/A

N/A

N/A

20%

15%

10%

5%

N/A 0%

0.0% 0-5

5-10

10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50

>50

Depth (m)

S10

0-5

5-10

10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50 Depth (m)

>50

2.0%

0.60%

Southern Baltic Proper Frequency of hypoxic profiles

Frequency of hypoxic profiles

Eastern Gotland basin 1.5%

1.0%

0.5%

N/A

N/A

N/A

0.50% 0.40% 0.30% 0.20% 0.10%

N/A

0.0%

0.00% 0-5

5-10

10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50

>50

0-5

5-10 10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50

Depth (m) 4.0%

30.0%

The Sound

25.0%

Frequency of hypoxic profiles

Frequency of hypoxic profiles

Belt Seas

20.0% 15.0% 10.0% 5.0% N/A

0.0%

N/A

N/A

3.0%

2.0%

1.0%

N/A

N/A

N/A

N/A

N/A

N/A

0.0%

0-5

5-10 10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50 >50

0-5

5-10

Depth (m)

10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50 Depth (m)

>50

40%

40%

Limfjord Frequency of hypoxic profiles

The Kattegat Frequency of hypoxic profiles

>50

Depth (m)

30%

20%

10%

N/A

30%

20%

10%

N/A

N/A

N/A

N/A

N/A

N/A

0%

0% 0-5

5-10 10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50

>50

Depth (m)

0-5

5-10

10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50 Depth (m)

>50

Figure S4. Depth-distribution of profiles with hypoxia (< 2 mg l-1) relative to the total number of profiles for the 14 regions delimited in Figure S1.

S11

15

15

5

5

The Quark

0

Difference

Months

Months 5

2

6

1

9

-1

8

-1

7 9

6 5

6

4 3

3

Surface Bottom Difference

2 1

0 -2 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010

0 0 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010

Months

Months

6

4 3

6

2 Surface Bottom Difference

1

Months

6

1 0

3

-1

Surface -1

Bottom Difference

6

2

3

Surface Bottom Difference

1

7 6

12

-1

Difference (mg l )

2

Concentration (mg l )

4 3

3

Western Gotland basin

12 9

9

15

5

Gulf of Riga

4

0 0 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010 Months

0 0 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010

15

12

-1

5 9

5

Gulf of Finland Concentration (mg l )

12

3

15

7

Finnish Archipelago

-1

15

Difference (mg l- 1)

Bottom Difference

12

5 9

4 3

6

2 3

Surface Bottom Difference

1

0 0 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010 Months

0 -2 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010 Months

S12

-1

Surface

0

Concentration (mg l )

9

Difference (mg l-1)

3

10

Stockholm Archipelago

4

12

3

15

Difference (mg l )

Concentration (mg l-1)

0

0 -1 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010

Bothnian Sea

Concentration (mg l- 1)

Surface Bottom Difference

0 -1 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010

15

Concentration (mg l- 1)

1 3

Difference (mg l )

Surface Bottom

2 6

Difference (mg l-1)

1 3

3 9

-1

2 6

4

12

Difference (mg l )

3 9

Concentration (mg l-1)

4

12

Difference (mg l-1)

Concentration (mg l-1)

Bothnian Bay

2 1 0

Surface Bottom Difference

5 9

4 3

6

2 3

-1

Surface Bottom Difference

1

0 -2 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010

0 0 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010

Months

Months 15

7

3

6 Surface Bottom Difference

2

-1

1

0 0 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010

9

4 3

6

2 3

0

Surface

5

Limfjord

4 3

6

2 3

Surface Bottom Difference

1

0 0 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010 Months

Concentration (mg l- 1)

-1

5

Difference (mg l - 1)

6

9

0

15

7

The Kattegat 12

1

Bottom Difference

1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010 Months

Months 15

5

Difference (mg l- 1)

-1

4

6

12

12

4

9

3

6

2

3

0

Surface Bottom Difference

Difference (mg l - 1)

9

Difference (mg l )

5

Concentration (mg l )

6

12

3

7

The Sound

Belt Seas

Concentration (mg l )

6

12

-1

3

6

Concentration (mg l )

Difference (mg l- 1)

4 9

3

7

Southern Baltic Proper

5

-1

Concentration (mg l )

12

15

Concentration (mg l- 1)

15

6

-1

7

Eastern Gotland basin

Difference (mg l )

15

1

0

1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010 Months

Figure S5. Trends in surface and bottom water oxygen concentration as well as their difference for the 14 regions delimited in Figure S1 using the seasonal windows defined in Table S2. Bottom oxygen means were calculated only when the density difference between surface and bottom was above 0.5, i.e. indicative of a stratified water column. All sites, including both sites with and without hypoxia, were included.

S13