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1 ALGAL SITUATION IN MARINE WATERS SURROUNDING SWEDEN AlgA ware Oceanographic Unit No 9, 15 – 20 November 2011 Sammanfattning De integrerade klorofyll a värdena (0-20m) i Skagerrak var inom det normala för årstiden. I Kattegatt återfanns däremot förhöjda klorofyll a värden vid N14 samt vid provtagningstillfälle två vid Anholt E. Växtplanktonsamhället i Skagerrak och Kattegatt dominerades i november dels av stora mängder av olika små cryptomonader men även relativt stora mängder av stora dinoflagellater tillhörande släktet Ceratium. Artdiversiteten var dock överlag låg. I Östersjön var de integrerade klorofyll a värdena (0-20m) höga för årstiden och översteg tioårsmedel vid de sydliga samt östliga stationerna. Endast vid de nordliga stationerna återfanns lägre klorofyll a halter. Cryptomonader och Pyramimonas spp. dominerade i Östersjön. På ett flertal stationer hittades även släktet Coscinodiscus i såpass stor omfattning att det är värt att nämnas. Chrysochromulina observerades i relativt stor mängd mellan Öland och Gotland. Filament av Cyanobakteriesläktet Aphanizomenon flos-aqua återfanns vid ett par stationer. Abstract e integrated (0-20 meters) chlorophyll a concentrations were normal for the season at all Skagerrak sites. Chlorophyll a concentrations were however above normal in Kattegat at N14 and on the second sampling occasion at Anholt E. e phytoplankton community in the Skagerrak and the Kattegat was dominated by several species of small cryptomonads, but also quite high numbers of the large dinoflagellates Ceratium were found. e species diversity was however low. e integrated (0-20 meters) chlorophyll a concentrations were high and above normal for the season in the southern and eastern parts of the Baltic Sea. Cryptomonads, and Pyramimonas spp. dominated in the Baltic Sea. e large diatom genus Coscinodiscus was found with relatively high numbers at several stations. High cell numbers of the genus Chrysochromulina was found between the islands Öland and Gotland. Some filaments of the cyanobacteria genus Aphanizomenon flos-aqua were observed at a couple of stations. 9 o E 12 o E 15 o E 18 o E 21 o E 54 o N 55 o N 56 o N 57 o N 58 o N 59 o N 60 o N Date: 2011 - 11 - 15 to 2011 - 11 - 20 A D P Pc N Az Cc Pm Plankton station High chl-a >4.5 chl-a >2.3 <=4.5 chl-a >=1.1 <=2.3 chl-a >=0.4 <1.1 Low chl-a <0.4 No chl-a sampling Algae harmful to fish Alexandrium spp. Dinophysis spp. Pseudo-nitzschia Pseudochattonella Nodularia Aphanizomenon Chrysochromulina Prorocentrum min Å17 Å15 Å13 Släggö P2 Fladen Anholt E W Landskrona BY1 BY2 Hanö Bight BY4 BY5 BCS III-10 BY10 BY15 BY20 BY32 BY38 N14 Falkenberg REF M1V1 BY29 BY31 Cc Cc

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ALGAL SITUATION INMARINE WATERS SURROUNDING SWEDEN

AlgAware Oceanographic Unit No 9, 15 – 20 November 2011

SammanfattningDe integrerade klorofyll a värdena (0-20m) i Skagerrak var inom det normala för årstiden. I Kattegatt återfanns däremot förhöjda klorofyll a värden vid N14 samt vid provtagningstillfälle två vid Anholt E.

Växtplanktonsamhället i Skagerrak och Kattegatt dominerades i november dels av stora mängder av olika små cryptomonader men även relativt stora mängder av stora dinoflagellater tillhörande släktet Ceratium. Artdiversiteten var dock överlag låg.

I Östersjön var de integrerade klorofyll a värdena (0-20m) höga för årstiden och översteg tioårsmedel vid de sydliga samt östliga stationerna. Endast vid de nordliga stationerna återfanns lägre klorofyll a halter.

Cryptomonader och Pyramimonas spp. dominerade i Östersjön. På ett flertal stationer hittades även släktet Coscinodiscus i såpass stor omfattning att det är värt att nämnas. Chrysochromulina observerades i relativt stor mängd mellan Öland och Gotland. Filament av Cyanobakteriesläktet Aphanizomenon flos-aqua återfanns vid ett par stationer.

AbstractThe integrated (0-20 meters) chlorophyll a concentrations were normal for the season at all Skagerrak sites. Chlorophyll a concentrations were however above normal in Kattegat at N14 and on the second sampling occasion at Anholt E.

The phytoplankton community in the Skagerrak and the Kattegat was dominated by several species of small cryptomonads, but also quite high numbers of the large dinoflagellates Ceratium were found. The species diversity was however low.

The integrated (0-20 meters) chlorophyll a concentrations were high and above normal for the season in the southern and eastern parts of the Baltic Sea.

Cryptomonads, and Pyramimonas spp. dominated in the Baltic Sea. The large diatom genus Coscinodiscus was found with relatively high numbers at several stations. High cell numbers of the genus Chrysochromulina was found between the islands Öland and Gotland. Some filaments of the cyanobacteria genus Aphanizomenon flos-aqua were observed at a couple of stations.

9oE 12oE 15oE 18oE 21oE 54oN

55oN

56oN

57oN

58oN

59oN

60oN

Date: 2011 − 11 − 15 to 2011 − 11 − 20

A

D

P

Pc

N

Az

Cc

Pm

Plankton station

High chl−a >4.5

chl−a >2.3 <=4.5

chl−a >=1.1 <=2.3

chl−a >=0.4 <1.1

Low chl−a <0.4No chl−a samplingAlgae harmful to fish

Alexandrium spp.

Dinophysis spp.

Pseudo−nitzschia

Pseudochattonella

Nodularia

Aphanizomenon

Chrysochromulina

Prorocentrum min

Å17

Å15 Å13

Släggö

P2

Fladen

Anholt E

W Landskrona

BY1 BY2

Hanö Bight

BY4

BY5

BCS III−10

BY10

BY15

BY20BY32

BY38N14 Falkenberg

REF M1V1

BY29

BY31

CcCc

2

More detailed information on species composition and abundance

The Skagerrak

Å17 15th of November (open Skagerrak)The phytoplankton cell density was quite low as it has been during both September and October. Different species belonging to the cryptomonadales group dominated, and the most numerous species was Plagioselmis prolonga. The toxin producing species Azadinium spp. was observed. No diatoms were found.

Släggö 15th of November (Skagerrak coast)The species diversity and cell density were quite low. The dinoflagellate Ceratium lineatum, was present with rather high cell numbers but was outnumbered by different small cryptomonads.

The integrated (0-20 meters) chlorophyll a concentration was within normal for the season at Släggö. At the other Skagerrak stations the concentrations were below normal.

The Kattegat

N14 Falkenberg 16th of NovemberThe dinoflagellate species Ceratium lineatum dominated at this station with more than 100 000 cells per liter. Different cryptomonad species were common. The potentially toxic dinoflagellate genus Dinophysis was represented by several species with low cell numbers. Diatoms were scarce, but the genus Thalassiosira and the potentially toxic genus Pseudo-nitzschia were observed.

The integrated (0-20 meters) chlorophyll a concentration was relatively high due to the elevated concentrations at the surface and ten meters below.

Anholt E 16th and 20th of NovemberThe total cell number was higher on the first sampling occasion compared to the second. There were only minor differences in species composition between the two samplings. The dinoflagellate Ceratium lineatum was very common at the first visit whereas Ceratium tripos dominated within the Ceratium genus on the second stop. Cryptomonads, with emphasis on the genus Teleaulax dominated the cell counts on both occasions. The potentially toxic flagellate Chrysochromulina was found with elevated cell numbers on the second occasion. The integrated (0-20 meters) chlorophyll a concentrations were within normal for the season at the first visit and above normal at the second. The chlorophyll a values did not correspond well to the cell counts.

The dinoflagellate Ceratium lineatum is one of several Ceratium species forming a massive bloom along the Swedish west coast this autumn. The species was com-mon at Släggö, N14 and Anholt E.

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The Baltic Sea

The phytoplankton community in the Baltic Sea was mainly dominated by small flagellates such as cryptomonads and Pyramimonas spp.. The diatom genus Coscinodiscus was common. High cell numbers of the genus Chrysochromulina, potentially toxic for fish and other organisms, were found at BY 38 between Öland and Gotland. Some filaments of the cyanobacteria species Aphanizomenon flos-aqua were observed in the northern part of the sampling route and between Öland and Gotland (BY 38).

The integrated (0-20 meters) chlorophyll a concentrations were above normal for the season in the southern and eastern part of the Baltic Sea. In the western part the concentrations were lower, but within normal.

Phytoplankton analysis and text by:Marie Johansen

The diatom Coscinodiscus granii.

4

Selection of observed species Å17 Släggö N14 Anholt E Anholt E

Red=potentially toxic species 15/11 15/11 16/11 16/11 20/11

cells/l cells/l cells/l cells/l cells/l

Ceratulina pelagica present

Dactyliosolen fragilissimus present

Guinardia delicatula present present present

Leptocylindrus minimus

Nitzschia longissima present

Proboscia alata present

Pseudo-nizschia spp. present

Skeletonema marinoi present present

Thalassiosira punctigera present present

Thalassiosira rotula present

Thalassiosira spp. present present

Amphidinium sphenoides present

Azadinium spp. cf present

Ceratium furca present

Ceratium fusus present present present present

Ceratium lineatum present common very common common present

Ceratium longipes present

Ceratium tripos present common common common common

Claddopyxis claytonii present

Dinophysis acuminata present present

Dinophysis acuta present present present

Dinophysis norvegica present present present present

Dinophysis rotundata present

Gymnodiniales common common present present present

Gyrodinium spirale present

Heterocapsa spp. present present present

Karenia mikimotoi present

Katodinium glaucum present present present present

Lingulodinium polyedrum present

Oxytoxum spp. present

Peridiniales common present present

Prorocentrum micans present present

Protoperidinium spp. present

Protoperidinium steinii present

Dichtyocha speculum present present common common

Chrysochromulina spp. present common

Chlorodendrales present

Cryptomonadales spp. present common

Hemiselmis virescens present present

Plagioselmis prolonga very common very common common common common

Teleaulax spp. present very common common very common very common

Pyramimonas spp. common present present very common present

Leucocryptos marina common present present common

Choanoflagellidea present

Ciliophora present present present present present

Laboea strobila presentMesodinium rubrum present present present

5

Selection of observed species BY2 BY5 BCS III-10 BY15 BY29 BY38 BY31 Ref. M1-V1

Red=potentially toxic species 17/11 17/11 17/11 18/11 18/11 19/11 19/11 18/11

cells/l cells/l cells/l cells/l cells/l cells/l cells/l cells/l

Actinocyclus spp. present

Chaetoceros danicus present present present present

Chaetoceros impressus present present present

Coscinodiscus cf. granii present present present present present

Cyclotella choctawhatcgeeana present present

Skeletonema marinoi present

Thalassiosira spp. present

Dinophysis acuminata present

Dinophysis norvegica present present

Gymnodiniales present present present present

Gyrodinium spirale present present

Heterocapsa spp. common

Katodinium glaucum present present present

Peridiniales present

Protoperidinium spp. present

Cryptomonadales spp. present present present present present

Hemiselmis virescens common present common present present

Plagioselmis prolonga very common very common common common present common present very common

Teleaulax spp. present common common common present common presentChrysochromulina spp. present present present present present very common present

Cyanobacteria colony forming common

Aphanizomenon flos-aquae common present present

Pseudanabaena spp. common present present present

Pyramimonas spp. present present very common present common common

Choanoflagellidea present present present common present presentLeucocryptus marina present present

Ciliophora present common common present present common present present

Mesodinium rubrum present common common present present common common present

6

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15Å17 Chl−a mean 0−20 m (µg/l)

chl−

a (µ

g/l)

Mean 2000 to 2009St.d. 2000 to 2009Chl mean valueRecent chl profile

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−15

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15Å15

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−15

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15Å13

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−15

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15Släggö

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−15

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15P2

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−15

The Skagerrak

0

10

20

30

40

50

7

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15Fladen Chl−a mean 0−20 m (µg/l)

chl−

a (µ

g/l)

Mean 2000 to 2009St.d. 2000 to 2009Chl mean valueRecent chl profile

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−16

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15N14 Falkenberg

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−16

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15Anholt E

chl−

a (µ

g/l)

0 2 4 6 8 10 12 14 16dot: Chl−a (µg/l)

2011

−11

−(1

6 in

bla

ck/2

0 in

gre

en)

0

10

20

30

40

50

dept

h (m

)

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15W Landskrona

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−16

The Kattegat and the Sound

0

10

20

30

40

50

8

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15BY1 Chl−a mean 0−20 m (µg/l)

chl−

a (µ

g/l)

Mean 2000 to 2009St.d. 2000 to 2009Chl mean valueRecent chl profile

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−16

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15BY2 Arkona Deep

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−17

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15BY4 Christiansö

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−17

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15BY5 Bornholm Deep

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−17

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15Hanö Bay

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−20

The Southern Baltic

0

10

20

30

40

50

9

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15BCS III−10 Chl−a mean 0−20 m (µg/l)

chl−

a (µ

g/l)

Mean 2000 to 2009St.d. 2000 to 2009Chl mean valueRecent chl profile

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−17

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15BY10

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−18

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15BY15 Gotland Deep

chl−

a (µ

g/l)

0 2 4 6 8 1060

dot: Chl−a (µg/l)

2011

−11

−18

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15BY20 Fårö Deep

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−18

The Eastern Baltic

0

10

20

30

40

50

10

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15REF M1V1 Chl−a mean 0−20 m (µg/l)

chl−

a (µ

g/l)

Mean 2000 to 2009St.d. 2000 to 2009Chl mean valueRecent chl profile

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−20

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15BY38 Karlsö Deep

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−19

0

10

20

30

40

50

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0

5

10

15BY32 Norrköping Deep

chl−

a (µ

g/l)

0 2 4 6 8 10dot: Chl−a (µg/l)

2011

−11

−19

The Western Baltic

0

10

20

30

40

50

Om klorofylldiagrammenKlorofyll a är ett mått på mängden växtplankton. Prover tas från ett antal djup från U/F Argos. Data presenteras både från de fasta djupen och som medelvärden 0-20 m. Utöver resultaten från laboratorieanalyserna av vattenprover mäts klorofyll a som fluorescens från ett automatiskt instrument som sänks ned från fartyget. På så sätt kan djupt liggande, ibland, tunna lager av växtplankton observeras. Tekniska problem ombord satte stopp för månadens fluorescens-mätningar.

About the chlorophyll graphsChlorophyll a is sampled from several depths from the R/V Argos. Data is presented both from the discrete depths and as an average 0-20 m. In addition to the laboratory analysis from the water samples chlorophyll fluorescence is measured in continuous depth profiles from the ship. This is a way to observe thin layes of phytoplankton occuring below the surface. Chlorphyll fluorescence was not measured this month due to technical problems on board.

11

Om AlgAwareSMHI genomför ca en gång per månad expeditioner med U/F Argos i Östersjön och Västerhavet. Resultat baserade på semikvantitativ mikroskopanalys av planktonprover samt klorofyllmätningar presenteras kortfattat i denna rapport. Infor-mation från SMHI:s satellitövervakning av algblomningar finns på www.smhi.se.

About AlgAwareSMHI carries out monthly cruises with R/V Argos in the Baltic and the Kattegat/Skagerrak. Results from semi quantitative microscopic analysis of phytoplankton samples as well as chlorophyll measurements are presented in brief in this report. Information from SMHI:s satellite monitoring of algal blooms is found on www.smhi.se.

Översikt över några potentiellt skadliga alger och det aktuella giftets effekt. Overview of potentially harmful algae and effects of toxins. Manual on harmful marine microalgae (2003 - UNESCO Publishing).

Kartan på framsidan visar viktat medelvärde för klorofyll a, µg/l (0-20 m) vid de olika stationerna. Förekomst av skad-liga alger vid stationer där arter analyseras markeras med symbol. Då cirkeln är tom innebär detta att stationen inte provtagits.

The map on the front page shows weighted mean of chlorophyll a, µg/l (0-20 m) at sampling stations. Presence of harm-ful algae at stations where species analysis is performed is shown with a symbol An empty cirkel indicates that there has been no sampling at that station.

Art / Species Gift / Toxin Eventuella symptom Clinical symptomsAlexandrium spp. Paralytic

shellfish poisoning (PSP)

Milda symptom:Inom 30 min.:Stickningar eller en känsla av bedövning runt läpparna, somsprids gradvis till ansiktet och nacken; stickningar i fingertoppar och tår;Huvudvärk; yrsel, illamående, kräkningar, diarréExtrema symptom: Muskelförlamning; andningssvårigheter; känsla av att kvävas;Man kan vara död inom 2-24 timmar efter att ha fått i sig giftet, på grund av att andningsmuskulaturen förlamas.

Mild case:Within 30 min:tingling sensation or numbness around lips, gradually spreading to face and neck; prickly sensation in fingertips and toes; headake, dizziness, nausea, vomiting, diarrhoea.Extreme caseMuscular paralysis; pronounced respiratory difficulty; choking sensation; death trough respiratory paralysis may occur within 2-24 hours after ingestion.

Dinophysis spp. Diarrehetic shellfish poisoning (DSP)

Milda symptom:Efter cirka 30 minuter till några timmar: yrsel, illamående, kräkningar, diarré, magontExtrema symptom: Upprepad exponering kan orsaka cancer

Mild case:Within 30 min-a few hours:dizziness, nausea, vomiting, diarrhoea, abdominal pain. Extreme case:Repeated exposure may cause cancer.

Pseudo- niztschia spp.

Amnesic shellfish poisoning (ASP)

Milda symptom:Efter 3-5 timmar: yrsel, illamående, kräkningar, diarré, magkramperExtrema symptom: Yrsel, hallucinationationer, förvirring, förlust av korttidsminnet, kramper

Mild case:Within 3-5 hours: dizziness, nausea, vomiting, diarrhoea, abdominal cramps.Extreme case:dizziness, hallucinations, confusion, loss of memory, cramps.

Chaetoceros concavicornis/ C.convolutus

Mechanical damage through hooks on setae

Låg celltäthet:Ingen påverkan.Hög celltäthet:Fiskens gälar skadas, fisken dör.

Low cell numbers: No effect on fish.High cell numbers:Fish death due to gill damage.

Pseudochattonella spp.

Fish toxin Låg celltäthet:Ingen påverkan.Hög celltäthet:Fiskens gälar skadas, fisken dör.

Low cell numbers: No effect on fish.High cell numbers:Fish death due to gill damage.

12

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