“…Few machine learning techniques for modeling the probability of toxic algae have been explored, including GLM (Anderson et al, 2011), decision trees (Bouquet et al, 2022), and GBM (Klemm et al, 2022). We demonstrate that SVM is a highly reliable approach for estimating the presence and HA probability of toxic algae in Norwegian coastal waters.…”
Section: Discussionmentioning
confidence: 99%
“…and Dinophysis spp. are commonly associated with stratified waters (Klemm et al, 2022; Reguera et al, 2012). The simulated response supports these associations, as the presence probability of D. acuminata , Alexandrium spp., and A. tamarense increases in shallower MLD—commonly correlated with more stratified waters.…”
Section: Discussionmentioning
confidence: 99%
“…Assessing geographical regions and time periods with an elevated probability of toxic species detection can offer several advantages, such as optimizing monitoring programs by redistributing resources and efforts, enhancing the protection of public health, enabling early harvesting prior to toxin outbreaks, improving business planning and investment decisions, and fostering increased consumer confidence (Jin et al, 2020). Probabilistic models can serve this purpose and inform likelihood changes based on external factors that influence the growth of toxic algae, such as sea surface temperature (SST), mixed layer depth (MLD), photosynthetic active radiation (PAR), and sea surface salinity (SSS) (Anderson et al, 2011(Anderson et al, , 2012Bates et al, 2018;García-Portela et al, 2018;Jauffrais et al, 2013;Kim et al, 2008;Klemm et al, 2022;Paz et al, 2006;Reguera et al, 2012).…”
Section: Introductionmentioning
confidence: 99%
“…(Bouquet et al, 2022). In Irish coastal waters, gradient boosting models (GBMs) were applied to model the probability of the presence/absence of A. tamarense using inputs such as temperature, salinity, and a water stratification index (Klemm et al, 2022). Although these studies have made significant contributions, none have addressed a wide range of toxic algae taxa, nor have they been calibrated for the Norwegian coastal shelf.…”
Section: Introductionmentioning
confidence: 99%
“…These inputs are chosen for two reasons: (i) they have enough time span and spatial coverage matching the algae observations in the shellfish farms and (ii) algae growth is mostly driven by these factors. Algae show distinct temperature-related traits that cause them to grow or diminish in different temperature ranges (Basti et al, 2018; Fehling et al, 2004; Guerrini et al, 2007; Nagai et al, 2004; Rial et al, 2023; Röder et al, 2012; Thomas et al, 2012); PAR corresponds to the light available for photosynthesis and therefore strongly influences algae growth (Bill et al, 2012; García-Portela et al, 2018; Jauffrais et al, 2013); salinity variations affect algae by inducing osmotic stress, creating ion stress through the unavoidable absorption or loss of ions, and altering the cellular ionic ratios due to selective mechanisms (Jauffrais et al, 2013; Kirst, 1990; Klemm et al, 2022; Nagai et al, 2004; Rial et al, 2023; Weber et al, 2021); shallower MLD—a common proxy to well-stratified waters—is commonly associated with HABs (Klemm et al, 2022; Reguera et al, 2012). Note that other important variables, such as nutrients, are not included as no product available matches the farms in a long time series.…”
We have developed probabilistic models to estimate the likelihood of harmful algae presence and outbreaks along the Norwegian coast, which can help optimization of the national monitoring program and the planning of mitigation actions. We employ support vector machines to calibrate probabilistic models for estimating the presence and harmful abundance (HA) of eight toxic algae found along the Norwegian coast, including Alexandrium spp., Alexandrium tamarense, Dinophysis acuta, Dinophysis acuminata, Dinophysis norvegica, Pseudo-nitzschia spp., Protoceratium reticulatum, and Azadinium spinosum. The inputs are sea surface temperature, photosynthetically active radiation, mixed layer depth, and sea surface salinity. The probabilistic models are trained with data from 2006 to 2013 and tested with data from 2014 to 2019. The presence models demonstrate good statistical performance across all taxa, with R (observed presence frequency vs. predicted probability) ranging from 0.69 to 0.98 and root mean squared error ranging from 0.84% to 7.84%. Predicting the probability of HA is more challenging, and the HA models only reach skill with four taxa (Alexandrium spp., A. tamarense, D. acuta, and A. spinosum). There are large differences in seasonal and geographical variability and sensitivity to the model input of different taxa, which are presented and discussed. The models estimate geographical regions and periods with relatively higher risk of toxic species presence and HA, and might optimize the harmful algae monitoring. The method can be extended to other regions as it relies only on remote sensing and model data as input and running national programs of toxic algae monitoring.
“…Few machine learning techniques for modeling the probability of toxic algae have been explored, including GLM (Anderson et al, 2011), decision trees (Bouquet et al, 2022), and GBM (Klemm et al, 2022). We demonstrate that SVM is a highly reliable approach for estimating the presence and HA probability of toxic algae in Norwegian coastal waters.…”
Section: Discussionmentioning
confidence: 99%
“…and Dinophysis spp. are commonly associated with stratified waters (Klemm et al, 2022; Reguera et al, 2012). The simulated response supports these associations, as the presence probability of D. acuminata , Alexandrium spp., and A. tamarense increases in shallower MLD—commonly correlated with more stratified waters.…”
Section: Discussionmentioning
confidence: 99%
“…Assessing geographical regions and time periods with an elevated probability of toxic species detection can offer several advantages, such as optimizing monitoring programs by redistributing resources and efforts, enhancing the protection of public health, enabling early harvesting prior to toxin outbreaks, improving business planning and investment decisions, and fostering increased consumer confidence (Jin et al, 2020). Probabilistic models can serve this purpose and inform likelihood changes based on external factors that influence the growth of toxic algae, such as sea surface temperature (SST), mixed layer depth (MLD), photosynthetic active radiation (PAR), and sea surface salinity (SSS) (Anderson et al, 2011(Anderson et al, , 2012Bates et al, 2018;García-Portela et al, 2018;Jauffrais et al, 2013;Kim et al, 2008;Klemm et al, 2022;Paz et al, 2006;Reguera et al, 2012).…”
Section: Introductionmentioning
confidence: 99%
“…(Bouquet et al, 2022). In Irish coastal waters, gradient boosting models (GBMs) were applied to model the probability of the presence/absence of A. tamarense using inputs such as temperature, salinity, and a water stratification index (Klemm et al, 2022). Although these studies have made significant contributions, none have addressed a wide range of toxic algae taxa, nor have they been calibrated for the Norwegian coastal shelf.…”
Section: Introductionmentioning
confidence: 99%
“…These inputs are chosen for two reasons: (i) they have enough time span and spatial coverage matching the algae observations in the shellfish farms and (ii) algae growth is mostly driven by these factors. Algae show distinct temperature-related traits that cause them to grow or diminish in different temperature ranges (Basti et al, 2018; Fehling et al, 2004; Guerrini et al, 2007; Nagai et al, 2004; Rial et al, 2023; Röder et al, 2012; Thomas et al, 2012); PAR corresponds to the light available for photosynthesis and therefore strongly influences algae growth (Bill et al, 2012; García-Portela et al, 2018; Jauffrais et al, 2013); salinity variations affect algae by inducing osmotic stress, creating ion stress through the unavoidable absorption or loss of ions, and altering the cellular ionic ratios due to selective mechanisms (Jauffrais et al, 2013; Kirst, 1990; Klemm et al, 2022; Nagai et al, 2004; Rial et al, 2023; Weber et al, 2021); shallower MLD—a common proxy to well-stratified waters—is commonly associated with HABs (Klemm et al, 2022; Reguera et al, 2012). Note that other important variables, such as nutrients, are not included as no product available matches the farms in a long time series.…”
We have developed probabilistic models to estimate the likelihood of harmful algae presence and outbreaks along the Norwegian coast, which can help optimization of the national monitoring program and the planning of mitigation actions. We employ support vector machines to calibrate probabilistic models for estimating the presence and harmful abundance (HA) of eight toxic algae found along the Norwegian coast, including Alexandrium spp., Alexandrium tamarense, Dinophysis acuta, Dinophysis acuminata, Dinophysis norvegica, Pseudo-nitzschia spp., Protoceratium reticulatum, and Azadinium spinosum. The inputs are sea surface temperature, photosynthetically active radiation, mixed layer depth, and sea surface salinity. The probabilistic models are trained with data from 2006 to 2013 and tested with data from 2014 to 2019. The presence models demonstrate good statistical performance across all taxa, with R (observed presence frequency vs. predicted probability) ranging from 0.69 to 0.98 and root mean squared error ranging from 0.84% to 7.84%. Predicting the probability of HA is more challenging, and the HA models only reach skill with four taxa (Alexandrium spp., A. tamarense, D. acuta, and A. spinosum). There are large differences in seasonal and geographical variability and sensitivity to the model input of different taxa, which are presented and discussed. The models estimate geographical regions and periods with relatively higher risk of toxic species presence and HA, and might optimize the harmful algae monitoring. The method can be extended to other regions as it relies only on remote sensing and model data as input and running national programs of toxic algae monitoring.
In recent years, blooms of the neurotoxic dinoflagellate Alexandrium catenella have been documented in Pacific Arctic waters, and the paralytic shellfish toxins (PSTs) that this species produces have been detected throughout the food web. These observations have raised significant concerns about the role that harmful algal blooms (HABs) will play in a rapidly changing Arctic. During a research cruise in summer 2022, a massive bloom of A. catenella was detected in real time as it was advected through the Bering Strait region. The bloom was exceptional in both spatial scale and density, extending > 600 km latitudinally, reaching concentrations > 174,000 cells L−1, and producing high‐potency PST congeners. Throughout the event, coastal stakeholders in the region were engaged and a multi‐faceted community response was mobilized. This unprecedented bloom highlighted the urgent need for response capabilities to ensure safe utilization of critical marine resources in a region that has little experience with HABs.
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