New approaches are required to undertake the substantial task of monitoring ongoing fishing activity in marine conservation areas to ensure conservation goals are achieved. To address this need, we applied previously developed, yet currently underused, vessel tracking methods based on Automatic Identification System (AIS) and aerial surveillance (“flyovers”) to Canada's Pacific marine conservation areas from 2012 to 2019. We used satellite and terrestrial‐based AIS receivers and flyover‐based visual observations to estimate illegal and legal fishing activity after 185 conservation area (CA) enactments (i.e., static, geographically defined areas with fishing regulations). We compared the effectiveness in detecting fishing activity between the AIS‐ and flyover‐based methods, and used the latter to determine that 93% of vessels were actively fishing in CAs without AIS. The AIS‐based method still detected 3303 h of fishing in CAs after enactment, and both methods estimated 22%–24% of fishing activity in CAs was illegal. The application of these methods also shed light on the complexity of fishing regulations across CAs (i.e., varying and CA‐specific restrictions). This highlighted the need to better align vessel tracking fishing gear classifications with CA regulation specifications, and conversely to simplify regulations (e.g., no‐take), for more accurate monitoring and evaluation moving forward.
Expansion of marine conservation areas (CA) necessitates resource‐efficient and achievable strategies for monitoring and evaluation of ongoing fishing activity at national levels. To demonstrate and explore such a strategy, we conducted the first extensive analysis of fishing activity within Canada's static, geographically defined marine CAs with fishing regulations (n = 264 areas). We used 8 years of Automatic Identification System data to estimate fishing effort across three oceans and conducted temporal and spatial comparisons specific to each CA's regulations and enactment date. We addressed questions on CA effectiveness, fishing displacement, fishing the line behavior, and relationships between fishing activity and spatial CA attributes. We estimated 22,000 h of fishing activity within CAs after enactments, 22% of which was identified as illegal. CA effectiveness appeared to be lowest for Atlantic CAs based on illegal fishing effort density within CAs. Fishing displacement and fishing the line was generally not apparent as buffer areas around CAs tended to already have higher fishing effort prior to enactments. CA effectiveness and responses to CAs varied considerably, as was visualized using timeseries plots and maps developed for each CA. Our evaluation of a nation's full suite of CAs provides managers with a foundation and approach for continued monitoring and reporting.
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