Anguilla rostrata has two juvenile stages, the elver and the glass eel. The glass eels migrate northward from the Sargasso Sea every year to reside in the fresh groundwater systems or the estuarine/brackish areas and return after maturation for breeding. The time at which it takes for eels to mature is dependent on both size and environmental conditions. This project was deigned to track temporal variance in abundance to indicate start, finish, and peak migration times of elvers and glass eels in Harry’s River, NL.

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Monitoring of the commercial eel harvest is an opportunistic practice that has been employed by Qalipu Mi’Kmaq First Nation Band for a number of years to collect, document or to track temporal variation/changes in the population dynamics of population information of the American eel (Anguilla rostrata). This includes individual weight, length, life stage ratio, and abnormalities such as red mouth and skin lesions. The American eel is a very culturally significant species for the Mi’kmaq people of Newfoundland. Along with being an important food source the American eel is also used for ceremonial and medicinal purposes. It is for these reasons that we are studying the local population in Muddy Hole, Western Newfoundland, and Little Horwood Brook, Central Newfoundland.

This project involves cooperating with local fish harvester’s in Western and Central Newfoundland and recording a number of biological characteristics of the eels captured by the harvester. Work was done through collaborating with local fish harvesters as to satisfy the community engagement portion of our Aboriginal Fisheries Strategy agreement. This opportunistic monitoring was beneficial to Qalipu, local harvesters and the eel population as additional nets were not set in the study areas. This reduced the amount of working hours required to complete the study, competition for catch with local harvesters, and stress on the eel population. Parks Canada employees also took part in monitoring at the western field site.

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The abundance of eelgrass (Zostera marina) was quantified at eight sites along the west coast of Newfoundland (NL), Canada. Two video procedures were employed to generate preliminary data on the percent cover of eelgrass. A GoPro high definition camera was mounted on a two meter 1.3cm diameter PVC pipe and attached 30 cm above a 19 x 19 cm quadrat. Still images were generated of quadrats or of the benthos during free swims. A 3 x 3 grid was added to the center of each image and the mean percent cover was calculated from these grids. The percent cover of eelgrass ranged between 5.89 and 69.27 %. Eelgrass abundance increased between June/July and September at sites 2, 4, and 7, before decreasing again in October at site 7. Overall, the percent cover of eelgrass peaked at 81.18% in September at site 4. Globally, sea grasses are declining in response to multiple stressors, including eutrophication, shoreline development, climate change, and aquatic invasive species. Eelgrass provides critical ecosystem services to coastal environments by stabilizing shorelines, contributing organic biomass to coastal food webs, and by increasing habitat heterogeneity along shallow subtidal shores. The degradation and loss of this highly productive habitat can have dire consequences for the stability and integrity of coastal environments in Atlantic Canada. Efforts to conserve this habitat will have long term benefits for populations of commercially, recreationally, and culturally important coastal species.

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The distribution and abundance of invasive colonial tunicates were documented at twelve sites along a ~270-km latitudinal gradient in western Newfoundland (NL), Canada. A combination of 10×10 and 15×15 cm polyvinyl chloride (PVC) panels were deployed on fixed and/or floating docks at each site between June and November 2014. The presence and abundance of invasive colonial tunicates were documented in September and November. Similar to patterns observed in 2013 (Caines personal observation), Botryllus schlosseri was found at Sites 1, 2 and 5, while Botrylloides sp. was observed at Site 2. Monthly sampling of 15×15 cm PVC panels, eelgrass (Zostera marina), rockweed (Fucus sp.), and kelp (Saccharina latissima) was conducted between September and November at Sites 1, 2 and 5 to determine spatial and temporal variation in the abundance of invasive colonial tunicates on artificial and natural substrates. Mean colony cover of B. schlosseri was 14.1 and 19.5% for panels sampled from floating docks in September for Sites 2 and 5, respectively, while mean cover of Botrylloides sp. was 3.7% on panels sampled from the fixed dock at Site 2. Interestingly, the frequency of occurrence for B. schlosseri colonies on rockweed increased from 20% in September to 100% in October at Site 2, while it decreased from 100% in September to 80% in October at Site 5. The frequency of Botrylloides sp. peaked at 50% and 70% on rockweed and kelp, respectively, in October at Site 2. The frequency of B. schlosseri on kelp specimens at Site 1 peaked at 40% in October, while kelp specimens from Site 2 had a peak colony frequency of 100% in September. Overall, the abundance of B. schlosseri on artificial and natural substrates was substantially lower at Site 1, which may be related to cooler sea temperature and increased wave exposure at this site.

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