4
Harmful algal blooms (HABs) have increased in abundance and severity around the world in recent decades. Among coastal HABs, benthic cyanobacteria (blue green algae) blooms, particularly Lyngbya spp., are becoming more numerous and persistent in tropical and subtropical marine embayments, estuaries, and reef environments. These species have become increasingly problematic in the near-shore waters of Florida, and it has been suggested that this may be in part caused by nutrient enrichment resulting from highly developed coastal habitats. Both climate change and anthropogenically derived nutrients provide the potential for increases in these nuisance blooms. Globally, blooms of Lyngbya have been linked to ecosystem and human health issues, including smothered corals and seagrass, reduced grazing by fish and invertebrates, and dermatitis and respiratory symptoms in humans. In a three-year study funded by the National Oceanographic and Atmospheric Administration’s Ecology of Harmful Algae Bloom Program (NOAA-ECOHAB), we examined the diversity, distribution, and abundance of Lyngbya in nearshore waters of southern Florida. Additionally, blooms on coral reefs off of Broward County and on seagrass and sediments near Sanibel-Captiva Island were investigated using an in situ nutrient bioassay approach that examined the effects of nitrate (N), phosphate (P), and biologically-available iron (Fe) on growth, carbon, nitrogen fixation, and secondary metabolite production in multiple Lyngbya spp. found in southern Florida, USA. 2009 Gulf of Mexico Atlantic Ocean 1 2 3 4 5 6 7 8 9 10 11 12 13 14 16 15 1. Sebastian Inlet 2. Indian River Lagoon 3. Jensen Beach 4. Lake Worth Lagoon 5. Hillsboro Inlet 6. Port Everglades Inlet 7. Dania Beach 8. Hollywood Beach 9. Biscayne Bay 10. Long Key 11. Big Pine Shoals 12. Kemp’s Channel 13. American Shoals 14. Dry Tortugas 15. Sanibel Island 16. Tampa Bay Bioassay study site Lyngbya Distribution Macro and microscopic morphology of Lyngbya spp. observed during summer months on Broward County reefs. Observations (168) of Lyngbya spp. were made throughout Florida. They were common in inshore habitats, particularly in the time period April-August. Lyngbya was observed as persistent blooms in the Indian River Lagoon, Broward County reefs, and Sanibel Island. At least four different species were identified in Floridian waters based on morphological characteristics: L. majuscula, L. confervoides, and two morphotypes of L. polychroa.

Lyngbya DistributionRight: Lyngbya overgrowing seagrass. Below: Primary productivity represented as 12 C uptake in L. majuscula bioassay at T 0, T 2, and T 4 (96 h incubation) after

  • Upload
    others

  • View
    3

  • Download
    0

Embed Size (px)

Citation preview

Page 1: Lyngbya DistributionRight: Lyngbya overgrowing seagrass. Below: Primary productivity represented as 12 C uptake in L. majuscula bioassay at T 0, T 2, and T 4 (96 h incubation) after

Dr. Hans Paerl: [email protected]. Valerie Paul: [email protected]. Judith M. O’Neil: [email protected]

PRINCIPAL INVESTIGATORS:

http://www.umces.edu

Harmful algal blooms (HABs) have increased in abundance and severity around the world in recent decades. Among coastal HABs, benthic cyanobacteria (blue green algae) blooms, particularly Lyngbya spp., are becoming more numerous and persistent in tropical and subtropical marine embayments, estuaries, and reef environments. These species have become increasingly problematic in the near-shore waters of Florida, and it has been suggested that this may be in part caused by nutrient enrichment resulting from highly developed coastal habitats. Both climate change and anthropogenically derived nutrients provide the potential for increases in these nuisance blooms. Globally, blooms of Lyngbya have been linked to ecosystem and human health issues, including smothered corals and seagrass, reduced grazing by fish and invertebrates, and dermatitis and respiratory symptoms in humans. In a three-year study funded by the National Oceanographic and Atmospheric Administration’s Ecology of Harmful Algae Bloom Program (NOAA-ECOHAB), we examined the diversity, distribution, and abundance of Lyngbya in nearshore waters of southern Florida. Additionally, blooms on coral reefs off of Broward County and on seagrass and sediments near Sanibel-Captiva Island were investigated using an in situ nutrient bioassay approach that examined the effects of nitrate (N), phosphate (P), and biologically-available iron (Fe) on growth, carbon, nitrogen fixation, and secondary metabolite production in multiple Lyngbya spp. found in southern Florida, USA.

Printed on 100% recycled paper

2009 The genus Lyngbya includes prolific producers of secondary metabolites, with over 200 compounds isolated from these cyanobacteria worldwide. Because these compounds often make cyanobacteria unpalatable to consumers, they are able to bloom under conditions of appropriate temperature, light, and nutrient availability. L. polychroa strains produce microcolins a and b, and when nutrients are replete, L. polychroa demonstrates a trade-off between secondary metabolite production and growth. At Sanibel, L. majuscula contained malyngolide- the first report of this toxic compound in Florida waters. When N, P, and chelated iron were added to growth chambers, L. majuscula was found to produce more malyngolide than in control treatments.

Enrichment of nitrogen, phosphorus, and iron can lead to increased growth, productivity, and changes in secondary metabolite concentration among different Lyngbya species. Since many of the secondary metabolites produced by Lyngbya can act as feeding deterrents to generalist grazers, these compounds may give Lyngbya a competitive advantage over other benthic algae. Subsequent blooms may inhibit the feeding of benthic grazers. The present study confirms and extends the results from other coastal studies, which indicate that both N and P inputs need to be controlled when non-N-fixing HABs co-occur (such as the red tide organism Karenia) with N-fixing cyanobacterial species. Therefore, we can conclude that single nutrient input controls are ineffective in addressing HAB ramifications. A larger-scale vision of both the ecosystems and the ecophysiology of these HABs is essential for setting thresholds for nutrient management strategies. Additionally, these results add to the growing body of knowledge that indicates the introduction of nutrients into the marine environment can not only increase the prevalence of HABs, but may also facilitate greater secondary metabolite production.

O

OOH

Malyngolide

Gulf of MexicoAtlantic Ocean1

23

4

567

89

1011

12

1314

16

15

1. Sebastian Inlet2. Indian River Lagoon3. Jensen Beach4. Lake Worth Lagoon5. Hillsboro Inlet6. Port Everglades Inlet7. Dania Beach8. Hollywood Beach9. Biscayne Bay10. Long Key11. Big Pine Shoals12. Kemp’s Channel13. American Shoals14. Dry Tortugas15. Sanibel Island16. Tampa Bay Bioassay study site

Lyngbya Distribution

References:Arthur, K.E., V.J. Paul, H.W. Paerl, J. M O’Neil, J. Joyner, and T. Meickle. (In press). Nutrient enrichment of the cyanobacterium Lyngbya spp.: Effect on growth, secondary metabolite concentration, and feeding by the specialist grazer Stylocheilus striatus. Mar. Ecol. Prog. Ser.Arthur, K.E., K. Semon, A. Capper, C. Ross, A.A. Erickson, S. Gunasekara, T. Meickle, S. Reed, J. Kwan, S. Matthew, H. Luesch, and V.J. Paul. (submitted) Distribution and chemical ecology of Lyngbya spp. (Cyanobacteria) in Florida, USA. Harmful Algae.Paerl, H.W., J.J. Joyner, A.R. Joyner, K. Arthur, V.J. Paul, J.M. O’Neil, amd C.A. Heil. 2008. Co-occurrence of dinoflagellates and cyanobacteria harmful algal blooms in southwest Florida coastal waters: A case for dual nutrient (N and P) input controls. Mar. Ecol. Prog. Ser. 371: 143-153.Sharp, L., K.E. Arthur, L. Gu, D. Sherman, C. Ross, G. Harrison, T. Meickle, H. Luesch, S. Matthew, and V.J. Paul. 2009. Phylogenetic and chemical diversity of three chemotypes of bloom- forming Lyngbya species (Cyanobacteria: Oscillatoriales) from reefs of Southeastern Florida. Appl. Environ.Microbiol. 75: 2879-2888.

Mal

yng

olid

e (m

g.g

-1d

ry w

t Ly

ngby

a)

ANOVA: F = 5.096 df = 7 p < 0.001

0.0

0.5

1.0

1.5

2.0

2.5

Control +N +P +N&P +Fe +EDTA +Fe EDTA +All

a

ab

aa

ab ab ab

b

Treatment Malyngolide concentrations in treatment groups at the end of the 2007 5-day bioassay from L. majuscula, showing the cumulative effects of N, P, Fe, and EDTA.

www.johnsabia.com

Continued development along both sides of Florida’s coast continues to present nutrient management issues, which will affect future Lyngbya blooms.

Researchers: Dr. Jennifer Joyner, Dr. Karen Arthur, Alan Joyner, Dr. Angela Capper, Dr. Cliff Ross, and Dr. Cynthia HeilGraphics, design and layout by Judith M. O’Neil, Kris Beckert, and Alan Joyner

Acknowledgements: Sanibel-Captiva Consevation Marine Laboratory, Dr. Richard Bartleson, Nova Southeastern University Oceanographic Center, Dr. Richard E. Dodge, and Broward County Environmental Protection & Growth Management Department, Ken Banks

Based on NOAA ECOHAB research grant #NA05NOS4781194

Macro and microscopic morphology of Lyngbya spp. observed during summer months on Broward County reefs.

Observations (168) of Lyngbya spp. were made throughout Florida. They were common in inshore habitats, particularly in the time period April-August. Lyngbya was observed as persistent blooms in the Indian River Lagoon, Broward County reefs, and Sanibel Island. At least four different species were identified in Floridian waters based on morphological characteristics: L. majuscula, L. confervoides, and two morphotypes of L. polychroa.

Page 2: Lyngbya DistributionRight: Lyngbya overgrowing seagrass. Below: Primary productivity represented as 12 C uptake in L. majuscula bioassay at T 0, T 2, and T 4 (96 h incubation) after

Right: Lyngbya overgrowing seagrass.

Below: Primary productivity represented as 12C uptake in L. majuscula bioassay at T0, T2, and T4 (96 h incubation) after daily additions of N, P, Fe, EDTA and combinations of nutrients. Error bars represent + 1 SE (n = 5)

Change in biomass from control, N, P, Fe, and EDTA samples from May 2006 bioassay for L. polychroa from Fort Lauderdale reefs. Error bars are + 1 SE (n = 5)

Lyngbya at both Sanibel and Fort Lauderdale appears to prefer ammonium, which requires the least amount of energy for uptake. However, the ability of both species (L. majuscula and L. polychroa) to use all forms of nitrogen, as well as its ability to fix nitrogen, gives these cyanobacteria a competitive advantage over algae species that do not fix nitrogen.

Blooms of the species Lyngbya majuscula have been occurring on the seagrass beds and sediments of Florida’s Gulf Coastal region of Sanibel Island. These blooms can overgrow seagrass, potentially smothering other benthic organisms. Mangroves in this region are also adversely affected by Lyngbya. Results of the bioassay conducted in this study showed increased primary production with additions of N and P. Although L. majuscula is primarily a benthic species, the oxygen it produces by rapid photosynthesis can get trapped in the filaments, causing tufts to become buoyant. The tufts can dislodge from the bottom, float up to the surface of the water, and form rafts of material that washes up on beaches. This material-in addition to being unsightly-is malodorous as it rots and can maintain toxic properties deleterious to humans and animals even after drying.

Lyngbya has the ability to use atmospheric nitrogen (N2) for its cellular needs through the process of N-fixation, an energetically demanding process that requires high amounts of iron for the enzyme nitrogenase that mediates the process. Experiments from Sanibel indicate that bioavailable iron stimulates L. majuscula productivity and N-fixation. In addition to N-fixation, L. majuscula can also take up inorganic forms of nitrogen, such as ammonium, nitrate, and the organic form urea.

05

101520

25303540

0.05 0.1 0.5 1N concentration (µg atm N)

Upt

ake

(V x

100

0h-1

) NH4

L. majuscula

NO3

Urea

05

101520

25303540

0.05 0.1 0.5 1N concentration (µg atm N)

Upt

ake

(V x

100

0h-1

) NH4

NO3

Urea

NH4NO3Urea

L. polychroa

Primary productivity represented as 12C uptake in L. polychroa bioassay at T0, T2, and T4 after daily additions of N, P, Fe, and EDTA. Error bars represent + 1 SE (n = 5)

Bioassay results from Lyngbya (L. polychroa, shown here) from Fort Lauderdale showed increased primary productivity with additions of nitrogen and phosphorus together. Growth of the L. polychroa was significantly stimulated by additions of bioavailable iron. This may be due to increased N-fixation at this site, which is also supported by lower d15N (an indicator of atmospheric N2) values.

The coastal environments adjacent to Fort Lauderdale and Dania Beach, Florida, are also experiencing intense blooms of Lyngbya polychroa . This N-fixing cyanobacteria is responding to coastal inputs of iron , N, and P from sewage outfalls wastewater , development , and groundwater . In addition to their toxicity, these blooms are causing adverse condi-tions for nearby coral reefs .

Fe

FeFlorida’s Gulf Coastal region of Sanibel Island is being affected by blooms of the cyanobacteria Lyngbya majuscula , which fouls beaches and cause the death of seagrasses . These blooms are most likely due to nutrient inputs from development recreational activities , and groundwater . Study sites in 2006 and in 2007 revealed that both N and P and iron are essential in bloom formation, due to this species’ ability to fix and utilize atmospheric N.

X

Fe

Fe

Control + N +P +N&P +FeEDTA +All

Cha

nge

in b

iom

ass

(g)

0.0

0.5

-0.5

1.0

1.5ANOVA: F = 6.620

df = 5p < 0.001

a

a a

a

ab

b

Treatment

0

500

1,000

1,500

2,000

2,500

3,000

3,500

Control +N +P +N&P +FeEDTA +All

T2

T4

C up

take

(g d

ry w

eight

-1 h-1

)

Lyngbya polychroa

Treatment

0

50

100

150

200

250

Control +N +P +N&P +Fe +EDTA +FeEDTA +AllC

upta

ke (g

dry

wei

ght-1

h-1)

Lyngbya majuscula

Treatment

T2

T4

Page 3: Lyngbya DistributionRight: Lyngbya overgrowing seagrass. Below: Primary productivity represented as 12 C uptake in L. majuscula bioassay at T 0, T 2, and T 4 (96 h incubation) after

Right: Lyngbya overgrowing seagrass.

Below: Primary productivity represented as 12C uptake in L. majuscula bioassay at T0, T2, and T4 (96 h incubation) after daily additions of N, P, Fe, EDTA and combinations of nutrients. Error bars represent + 1 SE (n = 5)

Change in biomass from control, N, P, Fe, and EDTA samples from May 2006 bioassay for L. polychroa from Fort Lauderdale reefs. Error bars are + 1 SE (n = 5)

Lyngbya at both Sanibel and Fort Lauderdale appears to prefer ammonium, which requires the least amount of energy for uptake. However, the ability of both species (L. majuscula and L. polychroa) to use all forms of nitrogen, as well as its ability to fix nitrogen, gives these cyanobacteria a competitive advantage over algae species that do not fix nitrogen.

Blooms of the species Lyngbya majuscula have been occurring on the seagrass beds and sediments of Florida’s Gulf Coastal region of Sanibel Island. These blooms can overgrow seagrass, potentially smothering other benthic organisms. Mangroves in this region are also adversely affected by Lyngbya. Results of the bioassay conducted in this study showed increased primary production with additions of N and P. Although L. majuscula is primarily a benthic species, the oxygen it produces by rapid photosynthesis can get trapped in the filaments, causing tufts to become buoyant. The tufts can dislodge from the bottom, float up to the surface of the water, and form rafts of material that washes up on beaches. This material-in addition to being unsightly-is malodorous as it rots and can maintain toxic properties deleterious to humans and animals even after drying.

Lyngbya has the ability to use atmospheric nitrogen (N2) for its cellular needs through the process of N-fixation, an energetically demanding process that requires high amounts of iron for the enzyme nitrogenase that mediates the process. Experiments from Sanibel indicate that bioavailable iron stimulates L. majuscula productivity and N-fixation. In addition to N-fixation, L. majuscula can also take up inorganic forms of nitrogen, such as ammonium, nitrate, and the organic form urea.

05

101520

25303540

0.05 0.1 0.5 1N concentration (µg atm N)

Upt

ake

(V x

100

0h-1

) NH4

L. majuscula

NO3

Urea

05

101520

25303540

0.05 0.1 0.5 1N concentration (µg atm N)

Upt

ake

(V x

100

0h-1

) NH4

NO3

Urea

NH4NO3Urea

L. polychroa

Primary productivity represented as 12C uptake in L. polychroa bioassay at T0, T2, and T4 after daily additions of N, P, Fe, and EDTA. Error bars represent + 1 SE (n = 5)

Bioassay results from Lyngbya (L. polychroa, shown here) from Fort Lauderdale showed increased primary productivity with additions of nitrogen and phosphorus together. Growth of the L. polychroa was significantly stimulated by additions of bioavailable iron. This may be due to increased N-fixation at this site, which is also supported by lower d15N (an indicator of atmospheric N2) values.

The coastal environments adjacent to Fort Lauderdale and Dania Beach, Florida, are also experiencing intense blooms of Lyngbya polychroa . This N-fixing cyanobacteria is responding to coastal inputs of iron , N, and P from sewage outfalls wastewater , development , and groundwater . In addition to their toxicity, these blooms are causing adverse condi-tions for nearby coral reefs .

Fe

FeFlorida’s Gulf Coastal region of Sanibel Island is being affected by blooms of the cyanobacteria Lyngbya majuscula , which fouls beaches and cause the death of seagrasses . These blooms are most likely due to nutrient inputs from development recreational activities , and groundwater . Study sites in 2006 and in 2007 revealed that both N and P and iron are essential in bloom formation, due to this species’ ability to fix and utilize atmospheric N.

X

Fe

Fe

Control + N +P +N&P +FeEDTA +AllC

hang

e in

bio

mas

s (g

)0.0

0.5

-0.5

1.0

1.5ANOVA: F = 6.620

df = 5p < 0.001

a

a a

a

ab

b

Treatment

0

500

1,000

1,500

2,000

2,500

3,000

3,500

Control +N +P +N&P +FeEDTA +All

T2

T4

C up

take

(g d

ry w

eight

-1 h-1

)

Lyngbya polychroa

Treatment

0

50

100

150

200

250

Control +N +P +N&P +Fe +EDTA +FeEDTA +All

C up

take

(g d

ry w

eigh

t-1 h-1

)

Lyngbya majuscula

Treatment

T2

T4

Page 4: Lyngbya DistributionRight: Lyngbya overgrowing seagrass. Below: Primary productivity represented as 12 C uptake in L. majuscula bioassay at T 0, T 2, and T 4 (96 h incubation) after

Dr. Hans Paerl: [email protected]. Valerie Paul: [email protected]. Judith M. O’Neil: [email protected]

PRINCIPAL INVESTIGATORS:

http://www.umces.edu

Harmful algal blooms (HABs) have increased in abundance and severity around the world in recent decades. Among coastal HABs, benthic cyanobacteria (blue green algae) blooms, particularly Lyngbya spp., are becoming more numerous and persistent in tropical and subtropical marine embayments, estuaries, and reef environments. These species have become increasingly problematic in the near-shore waters of Florida, and it has been suggested that this may be in part caused by nutrient enrichment resulting from highly developed coastal habitats. Both climate change and anthropogenically derived nutrients provide the potential for increases in these nuisance blooms. Globally, blooms of Lyngbya have been linked to ecosystem and human health issues, including smothered corals and seagrass, reduced grazing by fish and invertebrates, and dermatitis and respiratory symptoms in humans. In a three-year study funded by the National Oceanographic and Atmospheric Administration’s Ecology of Harmful Algae Bloom Program (NOAA-ECOHAB), we examined the diversity, distribution, and abundance of Lyngbya in nearshore waters of southern Florida. Additionally, blooms on coral reefs off of Broward County and on seagrass and sediments near Sanibel-Captiva Island were investigated using an in situ nutrient bioassay approach that examined the effects of nitrate (N), phosphate (P), and biologically-available iron (Fe) on growth, carbon, nitrogen fixation, and secondary metabolite production in multiple Lyngbya spp. found in southern Florida, USA.

Printed on 100% recycled paper

2009 The genus Lyngbya includes prolific producers of secondary metabolites, with over 200 compounds isolated from these cyanobacteria worldwide. Because these compounds often make cyanobacteria unpalatable to consumers, they are able to bloom under conditions of appropriate temperature, light, and nutrient availability. L. polychroa strains produce microcolins a and b, and when nutrients are replete, L. polychroa demonstrates a trade-off between secondary metabolite production and growth. At Sanibel, L. majuscula contained malyngolide- the first report of this toxic compound in Florida waters. When N, P, and chelated iron were added to growth chambers, L. majuscula was found to produce more malyngolide than in control treatments.

Enrichment of nitrogen, phosphorus, and iron can lead to increased growth, productivity, and changes in secondary metabolite concentration among different Lyngbya species. Since many of the secondary metabolites produced by Lyngbya can act as feeding deterrents to generalist grazers, these compounds may give Lyngbya a competitive advantage over other benthic algae. Subsequent blooms may inhibit the feeding of benthic grazers. The present study confirms and extends the results from other coastal studies, which indicate that both N and P inputs need to be controlled when non-N-fixing HABs co-occur (such as the red tide organism Karenia) with N-fixing cyanobacterial species. Therefore, we can conclude that single nutrient input controls are ineffective in addressing HAB ramifications. A larger-scale vision of both the ecosystems and the ecophysiology of these HABs is essential for setting thresholds for nutrient management strategies. Additionally, these results add to the growing body of knowledge that indicates the introduction of nutrients into the marine environment can not only increase the prevalence of HABs, but may also facilitate greater secondary metabolite production.

O

OOH

Malyngolide

Gulf of MexicoAtlantic Ocean1

23

4

567

89

1011

12

1314

16

15

1. Sebastian Inlet2. Indian River Lagoon3. Jensen Beach4. Lake Worth Lagoon5. Hillsboro Inlet6. Port Everglades Inlet7. Dania Beach8. Hollywood Beach9. Biscayne Bay10. Long Key11. Big Pine Shoals12. Kemp’s Channel13. American Shoals14. Dry Tortugas15. Sanibel Island16. Tampa Bay Bioassay study site

Lyngbya Distribution

References:Arthur, K.E., V.J. Paul, H.W. Paerl, J. M O’Neil, J. Joyner, and T. Meickle. (In press). Nutrient enrichment of the cyanobacterium Lyngbya spp.: Effect on growth, secondary metabolite concentration, and feeding by the specialist grazer Stylocheilus striatus. Mar. Ecol. Prog. Ser.Arthur, K.E., K. Semon, A. Capper, C. Ross, A.A. Erickson, S. Gunasekara, T. Meickle, S. Reed, J. Kwan, S. Matthew, H. Luesch, and V.J. Paul. (submitted) Distribution and chemical ecology of Lyngbya spp. (Cyanobacteria) in Florida, USA. Harmful Algae.Paerl, H.W., J.J. Joyner, A.R. Joyner, K. Arthur, V.J. Paul, J.M. O’Neil, amd C.A. Heil. 2008. Co-occurrence of dinoflagellates and cyanobacteria harmful algal blooms in southwest Florida coastal waters: A case for dual nutrient (N and P) input controls. Mar. Ecol. Prog. Ser. 371: 143-153.Sharp, L., K.E. Arthur, L. Gu, D. Sherman, C. Ross, G. Harrison, T. Meickle, H. Luesch, S. Matthew, and V.J. Paul. 2009. Phylogenetic and chemical diversity of three chemotypes of bloom- forming Lyngbya species (Cyanobacteria: Oscillatoriales) from reefs of Southeastern Florida. Appl. Environ.Microbiol. 75: 2879-2888.

Mal

yng

olid

e (m

g.g

-1d

ry w

t Ly

ngby

a)

ANOVA: F = 5.096 df = 7 p < 0.001

0.0

0.5

1.0

1.5

2.0

2.5

Control +N +P +N&P +Fe +EDTA +Fe EDTA +All

a

ab

aa

ab ab ab

b

Treatment Malyngolide concentrations in treatment groups at the end of the 2007 5-day bioassay from L. majuscula, showing the cumulative effects of N, P, Fe, and EDTA.

www.johnsabia.com

Continued development along both sides of Florida’s coast continues to present nutrient management issues, which will affect future Lyngbya blooms.

Researchers: Dr. Jennifer Joyner, Dr. Karen Arthur, Alan Joyner, Dr. Angela Capper, Dr. Cliff Ross, and Dr. Cynthia HeilGraphics, design and layout by Judith M. O’Neil, Kris Beckert, and Alan Joyner

Acknowledgements: Sanibel-Captiva Consevation Marine Laboratory, Dr. Richard Bartleson, Nova Southeastern University Oceanographic Center, Dr. Richard E. Dodge, and Broward County Environmental Protection & Growth Management Department, Ken Banks

Based on NOAA ECOHAB research grant #NA05NOS4781194

Macro and microscopic morphology of Lyngbya spp. observed during summer months on Broward County reefs.

Observations (168) of Lyngbya spp. were made throughout Florida. They were common in inshore habitats, particularly in the time period April-August. Lyngbya was observed as persistent blooms in the Indian River Lagoon, Broward County reefs, and Sanibel Island. At least four different species were identified in Floridian waters based on morphological characteristics: L. majuscula, L. confervoides, and two morphotypes of L. polychroa.