| #Q001 | administrative | operational | guidance | Guideline Application to Limited Treatment Waters | recreational water | Jurisdictions may choose to apply these guidelines to other natural waters that are applying limited treatment (e.g., short-term application of disinfection for an athletic event) although applying the guidelines in these scenarios should be done with caution as indicator organisms are easier to disinfect then other disease-causing microorganisms (e.g. protozoan pathogens). | When applying guidelines to natural waters applying limited treatment | high |
| #Q002 | monitoring | reporting | recommended | Total Microcystins Measurement | recreational water | When measuring microcystins, it is important to measure total microcystins. This includes microcystins that are both dissolved in the water (extracellular) and bound within the cyanobacterial cells (intracellular). | When measuring microcystins | high |
| #Q003 | monitoring | health | recommended | Inclusion of Microcystin Variants | recreational water | In addition, although the guideline value is based on the toxicity assessment of microcystin-LR (MC-LR), all measurable microcystin variants, not just MC-LR, should be included in the analysis. | | high |
| #Q004 | administrative | operational | recommended | Cyanobacteria Management Plan Inclusion | recreational water | The assessment of risk and the resultant decision on management of cyanobacteria and their toxins (including bloom prevention strategies) should be included as part of a management plan for the recreational area. | | high |
| #Q005 | administrative | operational | guidance | Modification of Guideline Values | recreational water | The responsible authority may modify these guideline values for recreational areas where site-specific information is available on the maximum ratio of microcystins to total cyanobacteria cells, cyanobacterial biovolume, or chlorophyll-a. | Where site-specific information is available on the maximum ratio of microcystins to total cyanobacteria cells, cyanobacterial biovolume, or chlorophyll-a | high |
| #Q006 | monitoring | operational | recommended | Monitoring Modified Guideline Values | recreational water | If values are modified, authorities should continue to monitor the maximum ratio of the parameter to microcystins to ensure that the modified values remain applicable. | If values are modified | high |
| #Q007 | administrative | operational | recommended | Identification of Areas Needing Management Plan | recreational water | Instead, responsible authorities should identify the areas that may need a management plan in place. | | high |
| #Q008 | administrative | operational | guidance | Identification of At-Risk Areas | recreational water | Responsible authorities can then use criteria to identify the areas that are at greater risk for bloom formation. | | high |
| #Q009 | administrative | operational | guidance | Prioritization and Monitoring Approach | recreational water | This information can then be used to prioritize areas that should be monitored for bloom formation and determine a monitoring approach (e.g., what to monitor, how often). | | high |
| #Q010 | monitoring | operational | recommended | Sampling Intensity Consideration | recreational water | Consideration should also be given to the intensity of sampling that is necessary for characterizing a waterbody and when this monitoring can be reduced based on an understanding of the site-specific conditions that may lead to cyanobacteria blooms. | | high |
| #Q011 | reporting | health | recommended | Public Reporting Encouragement | recreational water | As many recreational waterbodies in Canada will fall into the category of lower risk, the general public should be encouraged to report potential cyanobacteria issues to the responsible authority identified by the jurisdiction or to their local public health unit. | | high |
| #Q012 | monitoring | health | recommended | Routine Monitoring of Susceptible Areas | recreational water | Recreational water areas that are heavily used and that are suspected or are known to be susceptible to blooms should be routinely monitored as described in their monitoring plan (e.g., weekly or bi-weekly) and have an action plan in place for what measures to take in the event of a toxic bloom. | For recreational water areas that are heavily used and that are suspected or are known to be susceptible to blooms | high |
| #Q013 | administrative | operational | recommended | Action Plan Development | recreational water | It is very difficult to establish an action plan during a bloom event; prior discussion with local groups (e.g., other potentially affected parties, wildlife or agriculture agencies, analytical laboratories) is important to develop an appropriate action plan for use when/if it is needed. | | high |
| #Q014 | monitoring | operational | recommended | Validation of Alternative Monitoring Measures | recreational water | Other measures, such as molecular approaches or using satellite imagery, may also be included in a monitoring plan, although these methods should first be validated for the site. | | high |
| #Q015 | monitoring | operational | recommended | Confirmation of Cyanobacteria with Chlorophyll-a | recreational water | As chlorophyll-a is not specific to cyanobacteria, it is also important to confirm that blooms are cyanobacteria when using this indicator as part of a monitoring approach. | When using chlorophyll-a as part of a monitoring approach | high |
| #Q016 | monitoring | operational | recommended | Sampling During and After Bloom Collapse | recreational water | Sampling should be done during and after the collapse of the bloom in accordance with the recreational water management plan. | | high |
| #Q017 | administrative | health | recommended | Advice on Benthic Mats Accessibility | recreational water | Where mats are accessible, individuals should be advised to avoid these areas, including keeping pets away from the impacted areas. | Where mats are accessible | high |
| #Q018 | administrative | health | recommended | Precautionary Swimming/Contact Advisories | recreational water | In general, due to the difficulty in accurately characterizing the concentrations of toxins in a bloom, primary contact with recreational waters that contain visible blooms should be avoided, and a swimming/contact advisory should be issued as a precaution. | | high |
| #Q019 | administrative | operational | recommended | Consultation for Notifications | recreational water | The responsible authority in the jurisdiction, along with the recreational area’s cyanobacteria management plan, should be consulted for additional information. | | high |
| #Q020 | administrative | health | recommended | Duration of Swimming/Contact Advisories | recreational water | Swimming/contact advisories should remain in place until the potential health risk associated with the impacted area has been determined to be acceptable for recreational activities. | | high |
| #Q021 | administrative | operational | recommended | Conditions for Advisory Removal | recreational water | The conditions required to remove the swimming/contact advisory should be determined by the responsible authority based on the cyanobacteria management plan in place for the recreational area, or, in the absence of a recreational monitoring plan, based on site-specific information from the recreational area (e.g., dilution, historical occurrence of blooms). | | high |
| #Q022 | administrative | health | recommended | Advisory Duration in Absence of Toxin Testing | recreational water | In the absence of toxin testing, the swimming/contact advisory should remain in place long enough after the bloom has dissipated to allow any toxin present to be diluted or degraded. | In the absence of toxin testing | high |
| #Q023 | administrative | operational | mandatory | Determination of Toxin Dissipation Time | recreational water | The length of time required for toxin dissipation will need to be determined on a site-specific basis | | high |
| #Q024 | reporting | reporting | guidance | Seasonal Notifications for Reoccurring Blooms | recreational water | In waterbodies with a history of reoccurring blooms throughout the recreational season, responsible authorities may choose to leave notifications in place for the season once a bloom occurs. | In waterbodies with a history of reoccurring blooms throughout the recreational season | high |
| #Q025 | reporting | reporting | recommended | Clarity of Public Notifications | recreational water | Public notifications related to cyanobacteria blooms should be simple and clear. | | high |
| #Q026 | reporting | reporting | recommended | Contents of Public Notifications | recreational water | The notification should include (US EPA, 2021):
* the key message – closure or warning being issued or lifted
* list of approved activities and unsafe activities
* reason for the notification, e.g. high levels of cyanobacteria or cyanotoxins
* location of the recreational area affected by the notification
* potential consequences of contact with the affected area
* actions being taken by the beach managers to monitor the bloom
* contact information for individuals wanting additional information | | high |
| #Q027 | administrative | health | recommended | Provision of Educational Materials | recreational water | Educational materials outlining steps the public may take to reduce their personal risk in the event of a bloom should be provided. | | high |
| #Q028 | operational | health | recommended | Assumption of Bloom Toxicity | recreational water | As a result, any bloom encountered should be treated as potentially toxic. | | high |
| #Q029 | prohibition | health | recommended | Avoidance of Aerosol-Generating Activities | recreational water | As a precaution, activities that are known to generate significant amounts of aerosols (e.g. powerboating) and activities where accidental immersion risk is high (e.g. water skiing/tubing) should be avoided in areas containing visible cyanobacteria blooms. | In areas containing visible cyanobacteria blooms | high |
| #Q030 | treatment | operational | mandatory | Considerations for Control Measures | recreational water | Before direct or indirect measures are used, consideration needs to be given to the chemical, physical and biological characteristics of the watershed, as well as the costs, the environmental and social acceptability, and any regulatory requirements applicable to the approach being considered. | Before direct or indirect measures are used | high |
| #Q031 | treatment | operational | recommended | Scientific Evaluation for Cyanobacterial Control | recreational water | Only after a thorough scientific evaluation should a decision be made on the best solution for cyanobacterial control. | | high |
| #Q032 | monitoring | operational | recommended | Consideration of Cyanobacteria Types for Cell Counts | recreational water | Therefore, when using total cyanobacteria cell counts, it is important to also consider the types of cyanobacteria that are being identified and where possible, their potential for toxin production. | When using total cyanobacteria cell counts | high |
| #Q033 | monitoring | operational | recommended | Consideration of Cyanobacteria Types for Biovolume | recreational water | Similar to total cell counts, the types of cyanobacteria that are identified, as well as their potential for toxin production, should be considered to help avoid issuing unnecessary swimming/contact advisories. | | high |
| #Q034 | monitoring | operational | recommended | Awareness of Test Kit Cross-Reactivity | recreational water | The responsible authority should also be aware that some test kits detect both microcystins and nodularins. | | high |