Project Co-Investigators: Drs. Donald Anderson, Michael Brosnahan, and David Ralston (WHOI) and Katherine Hubbard (Florida Fish and Wildlife Conservation Commission)<\/strong><\/p>\n\t The emergence of toxic blooms of Pseudo-nitzschia <\/em>species and increased prevalence of domoic acid (DA) in shellfish has been a focus of WHCOHH. The first GOM shellfish closures for DA were in 2016, and observational data from cruises and coastal monitoring showed that the increased toxicity resulted from the predominance of P. australis <\/em>(Clark et al. 2019), <\/em>a species novel to the GOM [50] (Fig. 1). Analysis of environmental conditions showed that 2016 was not anomalous for water properties or forcing conditions that might explain the shift in bloom dynamics, but instead that introduction of P. australis<\/em> from outside the GOM was likely the key factor. Similarly, high DA levels closed shellfish beds in Narragansett Bay (RI) in 2017 for the first time, also linked to the novel presence of P. australis <\/em>(Sterling et al. 2022). To diagnose P. australis<\/em> in the GOM we used a regional circulation model with particle tracking to assess transport pathways, growth conditions, and source waters for P. australis<\/em>. Model results showed that the timing of observed DA toxicity- starting in the Bay of Fundy and then along the Maine coast – was consistent with transport of P. australis<\/em> from source waters on the Scotian Shelf (Clark et al. 2021) (Fig. 2). Monitoring of Pseudo-nitzschia<\/em> and DA has continued through WHCOHH since 2016, and P. australis<\/em> has remained a part of the seasonal progression of Pseudo-nitzschia<\/em> blooms. In 2016 the P. australis<\/em> bloom produced toxin at levels that far exceeded the other Pseudo-nitzschia<\/em> species, resulting in the high DA conditions (Clark et al. 2019). In subsequent years, toxin monitoring has recorded a steady decrease in shellfish DA despite the continued presence of P. australis <\/em>(Fig. 3). This suggests a changing relationship between species abundance and DA toxicity, perhaps due to nutrient availability (Clark et al. 2019).<\/p>\n In addition to the evolving HAB threat of P. australis<\/em>, WHCOHH research has continued to advance our understanding of A. catenella<\/em>. The resting cyst stage of A. catenella<\/em> provides an important control on bloom initiation, and the transition from dormancy to germination was long thought to be controlled by an endogenous clock (Anderson and Keafer 1987). However, studies of A. catenella<\/em> cysts from NM showed that temperature exposure through cumulative chilling determines the timing of the transition from dormancy into a quiescent state where cysts can germinate if conditions are favorable (Fischer et al. 2018). The conceptual framework of accumulated chilling controlling cyst quiescence affects bloom timing, with greater synchronization of germination and therefore more likely persistence of A. catenella<\/em> in locations with greater seasonal variability in temperature (Brosnahan et al. 2020). WHCOHH research also showed that temperature controls the timing of cyst germination once they are quiescent (Fischer and Brosnahan 2022). These radical revisions our understanding of cyst dynamics point to major role for water temperature to exert additional influence on bloom timing and intensity in the GOM and elsewhere.<\/p>\n Much of our understanding of A. catenella<\/em> dynamics is based on field, lab, and modeling studies of the GOM and NM, but with climate change we expect familiar patterns to shift. For example, Massachusetts Bay is a basin at the southern end of the GOM, and typically A. catenella<\/em> blooms are transported there from northerly sources via the coastal current (Franks and Anderson 1992; Anderson 1997). In recent years (2019-2021), the opposite has occurred, with larger blooms and earlier toxicity in Mass Bay than in waters to the north. The reasons for this are not yet known, and may be related to increased cyst abundance (D. Anderson, unpublished data), changes in cyst germination, or changes in circulation patterns within the Bay (Scully et al. 2022). Similarly, new evidence from WHCOHH points to the Arctic as a region where climate change is substantially increasing HAB risks. Surveys of the Chukchi Sea found extensive A. catenella<\/em> cysts beds that support recurrent local blooms (Anderson et al. 2021). Analysis indicates that the warming over the past two decades has increased cyst germination and advanced the timing of the bloom such that A. catenella<\/em> blooms could pose a significant threat to public and ecosystem health in Alaskan Arctic communities.<\/p>\n\t Project Lead: <\/strong>Dr. Dennis McGillicuddy<\/strong><\/a><\/p>\n Project Co-Investigators: Drs. Donald Anderson, Michael Brosnahan, and David Ralston (WHOI) and Katherine Hubbard (Florida Fish and Wildlife Conservation Commission)<\/strong><\/p>\n The emergence of toxic blooms of Pseudo-nitzschia <\/em>species and increased prevalence of domoic acid (DA) in shellfish has been a focus of WHCOHH. The first GOM shellfish closures for DA were in 2016, and observational data from cruises and coastal monitoring showed that the increased toxicity resulted from the predominance of P. australis <\/em>(Clark et al. 2019), <\/em>a species novel to the GOM [50] (Fig. 1). Analysis of environmental conditions showed that 2016 was not anomalous for water properties or forcing conditions that might explain the shift in bloom dynamics, but instead that introduction of P. australis<\/em> from outside the GOM was likely the key factor. Similarly, high DA levels closed shellfish beds in Narragansett Bay (RI) in 2017 for the first time, also linked to the novel presence of P. australis <\/em>(Sterling et al. 2022). To diagnose P. australis<\/em> in the GOM we used a regional circulation model with particle tracking to assess transport pathways, growth conditions, and source waters for P. australis<\/em>. Model results showed that the timing of observed DA toxicity- starting in the Bay of Fundy and then along the Maine coast – was consistent with transport of P. australis<\/em> from source waters on the Scotian Shelf (Clark et al. 2021) (Fig. 2). Monitoring of Pseudo-nitzschia<\/em> and DA has continued through WHCOHH since 2016, and P. australis<\/em> has remained a part of the seasonal progression of Pseudo-nitzschia<\/em> blooms. In 2016 the P. australis<\/em> bloom produced toxin at levels that far exceeded the other Pseudo-nitzschia<\/em> species, resulting in the high DA conditions (Clark et al. 2019). In subsequent years, toxin monitoring has recorded a steady decrease in shellfish DA despite the continued presence of P. australis <\/em>(Fig. 3). This suggests a changing relationship between species abundance and DA toxicity, perhaps due to nutrient availability (Clark et al. 2019).<\/p>\n In addition to the evolving HAB threat of P. australis<\/em>, WHCOHH research has continued to advance our understanding of A. catenella<\/em>. The resting cyst stage of A. catenella<\/em> provides an important control on bloom initiation, and the transition from dormancy to germination was long thought to be controlled by an endogenous clock (Anderson and Keafer 1987). However, studies of A. catenella<\/em> cysts from NM showed that temperature exposure through cumulative chilling determines the timing of the transition from dormancy into a quiescent state where cysts can germinate if conditions are favorable (Fischer et al. 2018). The conceptual framework of accumulated chilling controlling cyst quiescence affects bloom timing, with greater synchronization of germination and therefore more likely persistence of A. catenella<\/em> in locations with greater seasonal variability in temperature (Brosnahan et al. 2020). WHCOHH research also showed that temperature controls the timing of cyst germination once they are quiescent (Fischer and Brosnahan 2022). These radical revisions our understanding of cyst dynamics point to major role for water temperature to exert additional influence on bloom timing and intensity in the GOM and elsewhere.<\/p>\n Much of our understanding of A. catenella<\/em> dynamics is based on field, lab, and modeling studies of the GOM and NM, but with climate change we expect familiar patterns to shift. For example, Massachusetts Bay is a basin at the southern end of the GOM, and typically A. catenella<\/em> blooms are transported there from northerly sources via the coastal current (Franks and Anderson 1992; Anderson 1997). In recent years (2019-2021), the opposite has occurred, with larger blooms and earlier toxicity in Mass Bay than in waters to the north. The reasons for this are not yet known, and may be related to increased cyst abundance (D. Anderson, unpublished data), changes in cyst germination, or changes in circulation patterns within the Bay (Scully et al. 2022). Similarly, new evidence from WHCOHH points to the Arctic as a region where climate change is substantially increasing HAB risks. Surveys of the Chukchi Sea found extensive A. catenella<\/em> cysts beds that support recurrent local blooms (Anderson et al. 2021). Analysis indicates that the warming over the past two decades has increased cyst germination and advanced the timing of the bloom such that A. catenella<\/em> blooms could pose a significant threat to public and ecosystem health in Alaskan Arctic communities.<\/p>\n To quantitatively assess impacts of climate change on HABs, we have coupled downscaled climate models with regional models of circulation and bloom dynamics in the GOM. The approach was developed based on our review that emphasized using process-based models, dynamically downscaling climate influences, quantifying uncertainty, and incorporating long-term observations (Ralston and Moore 2020). We coupled the established GOM-scale model with dynamically downscaled climate model predictions for the Northwest Atlantic to assess changes in growth and transport for Pseudo-nitzschia<\/em> blooms (Clark et al. 2022). In the climate projections, inflows from the Scotian Shelf are predicted to increase, temperature increases will make conditions more favorable for P. australis<\/em>, and the Pseudo-nitzschia<\/em> species assemblage is likely to shift toward warmer adapted species. We have also coupled the downscaled climate model with the A. catenella<\/em> model for the GOM (Stock et al. 2005; He et al. 2008; Li et al. 2009). Preliminary results indicate that temperature increases will shift the A. catenella<\/em> bloom earlier in the year and increase maximum cell concentrations, particularly in the Eastern GOM. We have linked the A. catenella<\/em> model to a shellfish toxicity submodel based on comparisons with monitoring data and generated long-term hindcasts and climate projections of toxicity along the coast. In parallel, we have collected shellfish toxicity data from state monitoring programs in Maine, New Hampshire, and Massachusetts to develop indices of HAB intensity for the Eastern and Western GOM over the period 1980-2022 (Fig. 4). This index extends the previous record (Anderson et al. 2014) and creates a means for distinguishing interannual variability from climate-change trends.<\/p>\n \u00a0<\/strong><\/p>\n Bibliography and References Cited<\/strong><\/p>\n Anderson, Donald M. 1997. Bloom dynamics of toxic Alexandrium<\/em> species in the northeastern US. Limnology and Oceanography<\/em> 42: 1009-1022.<\/p>\n Anderson, Donald M., Darcie A. Couture, Judith L. Kleindinst, Bruce A. Keafer, Jr. McGillicuddy Dennis J., Jennifer L. Martin, Mindy L. Richlen, J. Michael Hickey, and Andrew R. Solow. 2014. Understanding interannual, decadal level variability in paralytic shellfish poisoning toxicity in the Gulf of Maine: The HAB Index. Deep Sea Research Part II: Topical Studies in Oceanography<\/em> 103. Harmful Algae in the Gulf of Maine: Oceanography, Population Dynamics, and Toxin Transfer in the Food Web: 264-276. doi:10.1016\/j.dsr2.2013.09.018.<\/p>\n Anderson, Donald M., Evangeline Fachon, Robert S. Pickart, Peigen Lin, Alexis D. Fischer, Mindy L. Richlen, Victoria Uva, et al. 2021. Evidence for massive and recurrent toxic blooms of Alexandrium catenella in the Alaskan Arctic. Proceedings of the National Academy of Sciences<\/em> 118. Proceedings of the National Academy of Sciences: e2107387118. doi:10.1073\/pnas.2107387118.<\/p>\n Anderson, Donald M., and Bruce A. Keafer. 1987. An endogenous annual clock in the toxic marine dinoflagellate Gonyaulax tamarensis<\/em>. Nature<\/em> 325: 616-617. doi:10.1038\/325616a0.<\/p>\n Brosnahan, Michael L., Alexis D. Fischer, Cary B. Lopez, Stephanie K. Moore, and Donald M. Anderson. 2020. Cyst-forming dinoflagellates in a warming climate. Harmful Algae<\/em> 91. Climate Change and Harmful Algal Blooms: 101728. doi:10.1016\/j.hal.2019.101728.<\/p>\n Clark, Suzanna, Katherine A. Hubbard, Donald M. Anderson, Dennis J. McGillicuddy Jr, David K. Ralston, and David W. Townsend. 2019. Pseudo-nitzschia bloom dynamics in the Gulf of Maine: 2012-2016. Harmful algae<\/em> 88. Elsevier: 101656.<\/p>\n Clark, Suzanna, Katherine A. Hubbard, Dennis J. McGillicuddy Jr, David K. Ralston, and Sugandha Shankar. 2021. Investigating Pseudo-nitzschia australis introduction to the Gulf of Maine with observations and models. Continental Shelf Research<\/em> 228. Elsevier: 104493.<\/p>\n Clark, Suzanna, Katherine A. Hubbard, David K. Ralston, Dennis J. McGillicuddy Jr, Charles Stock, Michael A. Alexander, and Enrique Curchitser. 2022. Projected effects of climate change on Pseudo-nitzschia bloom dynamics in the Gulf of Maine. Journal of Marine Systems<\/em> 230. Elsevier: 103737.<\/p>\n Fischer, Alexis D., and Michael L. Brosnahan. 2022. Growing Degree-Day Measurement of Cyst Germination Rates in the Toxic Dinoflagellate Alexandrium catenella. Applied and Environmental Microbiology<\/em> 88. American Society for Microbiology: e02518-21. doi:10.1128\/aem.02518-21.<\/p>\n Fischer, Alexis D., Michael L. Brosnahan, and Donald M. Anderson. 2018. Quantitative Response of Alexandrium catenella Cyst Dormancy to Cold Exposure. Protist<\/em> 169: 645-661. doi:10.1016\/j.protis.2018.06.001.<\/p>\n Franks, P. J. S., and Donald M. Anderson. 1992. Alongshore transport of a toxic phytoplankton bloom in a buoyancy current: Alexandrium tamarense<\/em> in the Gulf of Maine. Marine Biology<\/em> 112: 153-164. doi:10.1007\/BF00349739.<\/p>\n He, Ruoying, Dennis J. McGillicuddy, Donald M. Anderson, and Bruce A. Keafer. 2008. Historic 2005 toxic bloom of Alexandrium fundyense<\/em> in the western Gulf of Maine: 2. Coupled biophysical numerical modeling. Journal of Geophysical Research<\/em> 113: C07040. doi:10.1029\/2007JC004602.<\/p>\n Li, Yizhen, Ruoying He, Dennis J. McGillicuddy Jr., Donald M. Anderson, and Bruce A. Keafer. 2009. Investigation of the 2006 Alexandrium fundyense bloom<\/em> in the Gulf of Maine: In-situ observations and numerical modeling. Continental Shelf Research<\/em> 29: 2069-2082. doi:10.1016\/j.csr.2009.07.012.<\/p>\n Ralston, David K., and Stephanie K. Moore. 2020. Modeling harmful algal blooms in a changing climate. Harmful Algae<\/em> 91. Elsevier: 101729.<\/p>\n Scully, Malcolm E., W. Rockwell Geyer, David Borkman, Tracy L. Pugh, Amy Costa, and Owen C. Nichols. 2022. Unprecedented Summer Hypoxia in Southern Cape Cod Bay: An Ecological Response to Regional Climate Change? Biogeosciences Discussions<\/em>. Copernicus GmbH: 1-19.<\/p>\n Sterling, Alexa R., Riley D. Kirk, Matthew J. Bertin, Tatiana A. Rynearson, David G. Borkman, Marissa C. Caponi, Jessica Carney, et al. 2022. Emerging harmful algal blooms caused by distinct seasonal assemblages of a toxic diatom. Limnology and Oceanography<\/em> n\/a. doi:10.1002\/lno.12189.<\/p>\n Stock, Charles A., Dennis J. McGillicuddy Jr., Andrew R. Solow, and Donald M. Anderson. 2005. Evaluating hypotheses for the initiation and development of Alexandrium fundyense<\/em> blooms in the western Gulf of Maine using a coupled physical-biological model. Deep Sea Research Part II: Topical Studies in Oceanography<\/em> 52: 2715-2744. doi:10.1016\/j.dsr2.2005.06.022.<\/p>\n <\/p>\n <\/p>\n WHOI Ocean Topics<\/p>\n <\/p>\n A comprehensive resource for information about harmful algal blooms.<\/p>\n <\/p>\n Observations and commentary on the status of Paralytic Shellfish Poisoning (PSP) outbreaks in the northeast United States.<\/p>\n\t\t\t\t To quantitatively assess impacts of climate change on HABs, we have coupled downscaled climate models with regional models of circulation and bloom dynamics in the GOM. The approach was developed based on our review that emphasized using process-based models, dynamically downscaling climate influences, quantifying uncertainty, and incorporating long-term observations (Ralston and Moore 2020). We coupled the established GOM-scale model with dynamically downscaled climate model predictions for the Northwest Atlantic to assess changes in growth and transport for Pseudo-nitzschia<\/em> blooms (Clark et al. 2022). In the climate projections, inflows from the Scotian Shelf are predicted to increase, temperature increases will make conditions more favorable for P. australis<\/em>, and the Pseudo-nitzschia<\/em> species assemblage is likely to shift toward warmer adapted species. We have also coupled the downscaled climate model with the A. catenella<\/em> model for the GOM (Stock et al. 2005; He et al. 2008; Li et al. 2009). Preliminary results indicate that temperature increases will shift the A. catenella<\/em> bloom earlier in the year and increase maximum cell concentrations, particularly in the Eastern GOM. We have linked the A. catenella<\/em> model to a shellfish toxicity submodel based on comparisons with monitoring data and generated long-term hindcasts and climate projections of toxicity along the coast. In parallel, we have collected shellfish toxicity data from state monitoring programs in Maine, New Hampshire, and Massachusetts to develop indices of HAB intensity for the Eastern and Western GOM over the period 1980-2022 (Fig. 4). This index extends the previous record (Anderson et al. 2014) and creates a means for distinguishing interannual variability from climate-change trends.<\/p>\n \u00a0<\/strong><\/p>\n Bibliography and References Cited<\/strong><\/p>\n Anderson, Donald M. 1997. Bloom dynamics of toxic Alexandrium<\/em> species in the northeastern US. Limnology and Oceanography<\/em> 42: 1009-1022.<\/p>\n Anderson, Donald M., Darcie A. Couture, Judith L. Kleindinst, Bruce A. Keafer, Jr. McGillicuddy Dennis J., Jennifer L. Martin, Mindy L. Richlen, J. Michael Hickey, and Andrew R. Solow. 2014. Understanding interannual, decadal level variability in paralytic shellfish poisoning toxicity in the Gulf of Maine: The HAB Index. Deep Sea Research Part II: Topical Studies in Oceanography<\/em> 103. Harmful Algae in the Gulf of Maine: Oceanography, Population Dynamics, and Toxin Transfer in the Food Web: 264-276. doi:10.1016\/j.dsr2.2013.09.018.<\/p>\n Anderson, Donald M., Evangeline Fachon, Robert S. Pickart, Peigen Lin, Alexis D. Fischer, Mindy L. Richlen, Victoria Uva, et al. 2021. Evidence for massive and recurrent toxic blooms of Alexandrium catenella in the Alaskan Arctic. Proceedings of the National Academy of Sciences<\/em> 118. Proceedings of the National Academy of Sciences: e2107387118. doi:10.1073\/pnas.2107387118.<\/p>\n Anderson, Donald M., and Bruce A. Keafer. 1987. An endogenous annual clock in the toxic marine dinoflagellate Gonyaulax tamarensis<\/em>. Nature<\/em> 325: 616-617. doi:10.1038\/325616a0.<\/p>\n Brosnahan, Michael L., Alexis D. Fischer, Cary B. Lopez, Stephanie K. Moore, and Donald M. Anderson. 2020. Cyst-forming dinoflagellates in a warming climate. Harmful Algae<\/em> 91. Climate Change and Harmful Algal Blooms: 101728. doi:10.1016\/j.hal.2019.101728.<\/p>\n Clark, Suzanna, Katherine A. Hubbard, Donald M. Anderson, Dennis J. McGillicuddy Jr, David K. Ralston, and David W. Townsend. 2019. Pseudo-nitzschia bloom dynamics in the Gulf of Maine: 2012-2016. Harmful algae<\/em> 88. Elsevier: 101656.<\/p>\n Clark, Suzanna, Katherine A. Hubbard, Dennis J. McGillicuddy Jr, David K. Ralston, and Sugandha Shankar. 2021. Investigating Pseudo-nitzschia australis introduction to the Gulf of Maine with observations and models. Continental Shelf Research<\/em> 228. Elsevier: 104493.<\/p>\n Clark, Suzanna, Katherine A. Hubbard, David K. Ralston, Dennis J. McGillicuddy Jr, Charles Stock, Michael A. Alexander, and Enrique Curchitser. 2022. Projected effects of climate change on Pseudo-nitzschia bloom dynamics in the Gulf of Maine. Journal of Marine Systems<\/em> 230. Elsevier: 103737.<\/p>\n Fischer, Alexis D., and Michael L. Brosnahan. 2022. Growing Degree-Day Measurement of Cyst Germination Rates in the Toxic Dinoflagellate Alexandrium catenella. Applied and Environmental Microbiology<\/em> 88. American Society for Microbiology: e02518-21. doi:10.1128\/aem.02518-21.<\/p>\n Fischer, Alexis D., Michael L. Brosnahan, and Donald M. Anderson. 2018. Quantitative Response of Alexandrium catenella Cyst Dormancy to Cold Exposure. Protist<\/em> 169: 645-661. doi:10.1016\/j.protis.2018.06.001.<\/p>\n Franks, P. J. S., and Donald M. Anderson. 1992. Alongshore transport of a toxic phytoplankton bloom in a buoyancy current: Alexandrium tamarense<\/em> in the Gulf of Maine. Marine Biology<\/em> 112: 153-164. doi:10.1007\/BF00349739.<\/p>\n He, Ruoying, Dennis J. McGillicuddy, Donald M. Anderson, and Bruce A. Keafer. 2008. Historic 2005 toxic bloom of Alexandrium fundyense<\/em> in the western Gulf of Maine: 2. Coupled biophysical numerical modeling. Journal of Geophysical Research<\/em> 113: C07040. doi:10.1029\/2007JC004602.<\/p>\n Li, Yizhen, Ruoying He, Dennis J. McGillicuddy Jr., Donald M. Anderson, and Bruce A. Keafer. 2009. Investigation of the 2006 Alexandrium fundyense bloom<\/em> in the Gulf of Maine: In-situ observations and numerical modeling. Continental Shelf Research<\/em> 29: 2069-2082. doi:10.1016\/j.csr.2009.07.012.<\/p>\n Ralston, David K., and Stephanie K. Moore. 2020. Modeling harmful algal blooms in a changing climate. Harmful Algae<\/em> 91. Elsevier: 101729.<\/p>\n Scully, Malcolm E., W. Rockwell Geyer, David Borkman, Tracy L. Pugh, Amy Costa, and Owen C. Nichols. 2022. Unprecedented Summer Hypoxia in Southern Cape Cod Bay: An Ecological Response to Regional Climate Change? Biogeosciences Discussions<\/em>. Copernicus GmbH: 1-19.<\/p>\n Sterling, Alexa R., Riley D. Kirk, Matthew J. Bertin, Tatiana A. Rynearson, David G. Borkman, Marissa C. Caponi, Jessica Carney, et al. 2022. Emerging harmful algal blooms caused by distinct seasonal assemblages of a toxic diatom. Limnology and Oceanography<\/em> n\/a. doi:10.1002\/lno.12189.<\/p>\n Stock, Charles A., Dennis J. McGillicuddy Jr., Andrew R. Solow, and Donald M. Anderson. 2005. Evaluating hypotheses for the initiation and development of Alexandrium fundyense<\/em> blooms in the western Gulf of Maine using a coupled physical-biological model. Deep Sea Research Part II: Topical Studies in Oceanography<\/em> 52: 2715-2744. doi:10.1016\/j.dsr2.2005.06.022.<\/p>\n <\/p>\n <\/p>\n WHOI Ocean Topics<\/p>\n <\/p>\n A comprehensive resource for information about harmful algal blooms.<\/p>\n <\/p>\n Observations and commentary on the status of Paralytic Shellfish Poisoning (PSP) outbreaks in the northeast United States.<\/p>\n\n","protected":false},"excerpt":{"rendered":" Project 2: Climate forcing of harmful algal blooms and toxicity exposure in the Northeast U.S. Project Lead: Dr. Dennis McGillicuddy Project Co-Investigators: Drs. Donald Anderson, Michael Brosnahan, and David Ralston (WHOI) and Katherine Hubbard (Florida Fish and Wildlife Conservation Commission) The emergence of toxic blooms of Pseudo-nitzschia species and increased prevalence of domoic acid (DA)…<\/p>\n","protected":false},"author":50,"featured_media":0,"parent":0,"menu_order":0,"comment_status":"closed","ping_status":"closed","template":"","meta":[],"_links":{"self":[{"href":"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-json\/wp\/v2\/pages\/1359"}],"collection":[{"href":"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-json\/wp\/v2\/pages"}],"about":[{"href":"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-json\/wp\/v2\/types\/page"}],"author":[{"embeddable":true,"href":"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-json\/wp\/v2\/users\/50"}],"replies":[{"embeddable":true,"href":"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-json\/wp\/v2\/comments?post=1359"}],"version-history":[{"count":4,"href":"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-json\/wp\/v2\/pages\/1359\/revisions"}],"predecessor-version":[{"id":1378,"href":"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-json\/wp\/v2\/pages\/1359\/revisions\/1378"}],"wp:attachment":[{"href":"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-json\/wp\/v2\/media?parent=1359"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}![](\"https:\/\/web.archive.org\/web\/20240720133944im_\/https:\/\/www.whoi.edu\/cms\/images\/topics_redtide_x_256513.jpg\")
<\/a>Harmful Algae & Red Tides<\/a><\/h3>\n![](\"https:\/\/web.archive.org\/web\/20240720133944im_\/https:\/\/www.whoi.edu\/cms\/images\/topics_habs_website_x_117371_193933_256493.jpg\")
<\/a>WHOI’s Harmful Algae Website<\/a><\/h3>\n![](\"https:\/\/web.archive.org\/web\/20240720133944im_\/https:\/\/www.whoi.edu\/cms\/images\/topics_habs_website2_x_117375_193934_256456.jpg\")
<\/a>New England Harmful Algal Bloom\/Red Tide Information<\/a><\/h3>\n![\"Fig.](\"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-content\/uploads\/sites\/30\/2022\/11\/P2Fig1.jpg\" "\\"P2Fig1\\"")
\n\t\tFig. 1. ARISA-based Pseudo-nitzschia species abundance in (left) 2015 and (right) 2016. Pie size scaled by log(cell count) (scale in left panel). From [1]\n\t\t\t\t![\"Fig.](\"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-content\/uploads\/sites\/30\/2022\/11\/P2Fig2.jpg\")
\n\t\tFig. 2. Particle tracks (colored by date) released on the Scotian Shelf in a hindcast of 2016, illustrating connectivity potential of the fall bloom. From Clark et al. 2021.\n\t\t\t\t![\"Fig.](\"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-content\/uploads\/sites\/30\/2022\/11\/P2Fig3.jpg\" "\\"P2Fig3\\"")
\n\t\tFig. 3. (top) Time series of DA in shellfish and (bot.) P. australis fluorescence from ARISA. K. Hubbard, unpub. data.\n\t\t\t\t![\"Fig.](\"https:\/\/www2.whoi.edu\/site\/whcohh\/wp-content\/uploads\/sites\/30\/2022\/11\/P2Fig4.jpg\" "\\"P2Fig4\\"")
\n\t\tFig. 4. Western Maine HAB index as from [12] but extended through 2021 (blue), with the nodal amplitude of M2 tides on an inverted scale (red).\n\t<\/a>Harmful Algae & Red Tides<\/a><\/h3>\n<\/a>WHOI’s Harmful Algae Website<\/a><\/h3>\n<\/a>New England Harmful Algal Bloom\/Red Tide Information<\/a><\/h3>\n