AOFRC E-Newsletter 2014/2015 by Anishinabek/Ontario Fisheries Resource Centre

Message from the General Manager …………………………… 2 Funding Opportunities …………………………………………….. 3 2014/2015 Field Programs ………………………………………. 4 Fish Mix & Match ………………………………………………….. 16 Fish Recipes ……………………………………………… ..………17 For the Kids ………………………………………………………… 18

Baamaapii Kawaabmin!

Brought to you by: The Anishinabek/Ontario Fisheries Resource Centre

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

Message from the General Manager When the A/OFRC began operations in 1995, it was designed to serve as an independent body providing competent, transparent advice related to management of fisheries and the ecosystems supporting fisheries in the traditional territories of the Anishinabek

Nation. We continue to serve that purpose for the 39 First Nations communities of the Anishinabek Nation. There is no shortage of demand for what we do. Every year we receive more requests for work than our resources allow us to deliver. It’s a difficult matter to decide which communities have their projects approved and which do not. In addition to assessing projects on technical merits, we use a process that takes into account whether each region is receiving support, whether a community has had a project approved recently, whether a project is relevant to more than

one community and generally strives to treat all communities in a fair and balanced manner that addresses their needs in a timely fashion. We have learned a few things over the years about getting the work done and are proud of our record of successfully completing challenging projects. We are also proud of the many people who have gained valuable experience working on our crews either as participants in our internship programs or as seasonal staff. The projects described in this newsletter are examples of our work; there are many kinds of things we can do in your community to assist with managing your fishery or informing your other initiatives with assessments of fish populations and habitat. We look forward to working with you.

Board of Directors The A/OFRC is not-for-profit corporation controlled by a Board of Directors appointed by the Anishinabek Nation and the Ontario Ministry of Natural Resources and Forestry. The Centre serves as an independent source of information on fisheries conservation and management within traditional harvesting areas. The Ontario Minister of Natural Resources and Forestry and the Grand Chief of the Anishinabek Nation jointly approve the Chairperson.

A/OFRC Chairperson Cliff Meness, Algonquins of Pikwakanagan

OMNRF Appointments Sue Chiblow, Secretary/Treasurer Frank Kennedy, Retired Director of the Science and Information Branch, OMNRF Kevin Reid, Fisheries Scientist for the Ontario Commercial Fisheries Association Tom Whillans, Assoc. Professor, Environmental and Resource Studies, Trent University

Anishinabek Nation Appointments Rick Stevens, Nipissing First Nation Brian Monague, Chippewas of Kettle & Stony Point Lorenzo Whetung, Curve Lake First Nation Vacant Board Positions: - Superior Region

For More Information

Anishinabek/Ontario Fisheries Resource Centre 755 Wallace Road, Unit 5 North Bay, ON P1A 0E7 Phone: (705) 472-7888 Fax: (705) 472-6333 aofrc@aofrc.org www.aofrc.org

Answers to Fish Mix & Match 1F; 2C; 3A; 4B; 5D; 6G; 7E

Peter Meisenheimer

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

FUNDING OPPORTUNITIES! Need support with your application or project design? The A/OFRC works with communities within the Anishinabek Nation, and regularly supports clients in successfully applying for fisheries related funding opportunities and enhancing environmental and community capacity.

Great Lakes Guardian Community Fund As part of Ontario’s Great Lakes Strategy, this Fund was set up to help people take action to protect and restore their corner of the Great Lakes. The fund is open to not-for-profit organizations, First Nations communities and organizations, and Metis communities and organizations located within the areas of Lake Erie, Lake Huron, Lake Ontario, Lake Superior, St. Lawrence River, the Ottawa River, and their connecting channels and watersheds. Up to $25,000 per project is available. To learn more, visit http://www.ontario.ca/page/great-lakes-guardiancommunity-fund

Aboriginal Fund for Species at Risk The goal of this program is to contribute to the conservation and protection of Canada’s biodiversity by supporting species recovery planning, habitat protection, and overall conservation and capacity building initiatives by Aboriginal people in Canada. The key objective is to encourage meaningful involvement of Aboriginal people and communities in the implementation of the Species at Risk Act. Funding ranges from $10,000 to $50,000 per year, and projects may extend more than one year. To learn more, visit http://www.dfo-mpo.gc.ca/fm-gp/aboriginalautochtones/sar-lep/funds-fonds-eng.htm

First Peoples Worldwide: Keepers of the Earth Funds Intended to preserve, control, utilize, leverage, retain, create and increase Indigenous assets (eg. Land, culture, language, kinship networks, subsistence activities, and personal efficacy). Projects must be locally initiated—conceived and implemented in Indigenous communities. Grant amounts for first time applicants range from $500—$5000. Grants can be awarded up to three (3) consecutive times. After the first year, you project is like to be approved for a larger grant. To learn more, visit http://www.firstpeoples.org/grants/ application-guidelines

Recreational Fisheries Conservation Partnerships Program This program’s objective is to restore, rebuild, and rehabilitate recreational fisheries habitat. For more information, visit http:// www.dfo-mpo.gc.ca/pnw-ppe/rfcpp-ppcpr/index-eng.html to inquire about the eligibility of your project

Canada Ontario Resource Development Agreement The Canada Ontario Resource Development Agreement is an agreement between Canada, Ontario and First Nations members in Ontario. The agreement promotes resource and economic development initiatives for First Nation`s members by providing financial assistance to develop and utilize renewable natural resources. Funding up to $35,000. To learn more, visit http://www.anishinabek.ca/lands-and-resources-other.asp.

Seniors Community Grant Program This is the first grant program in Ontario dedicated solely to seniors, and is designed to give seniors more opportunities to participate in their communities by providing funding to not-for-profit community groups for projects that encourage greater social inclusion, volunteerism and community engagement for seniors. Grants range from $500 to $8000. Applications are accepted until March 4, 2016.

Great Lakes Sustainability Fund This fund provides technical and financial support to action projects aimed at cleaning up, restoring and protecting the environmental quality and beneficial uses of Canada’s Great Lakes in areas of concern. Projects are restricted to the Canadian Great Lakes Areas of Concern. Deadline: early December. For more information, visit https://www.ec.gc.ca/raps-pas/default.asp?lang=En&n=A290294A-1.

EcoAction Community Funding Program The EcoAction Community Funding Program funds projects across Canada to encourage Canadians to take action to address clean air, clean water, climate change and nature issues, and to build the capacity of communities to sustain these activities into the future. Up to $100,000 per project is available. Maximum duration of a project is 36 months. Deadline for submissions: November 1st. For more information, visit https://www.ec.gc.ca/ecoaction/

Ontario Trillium Foundation The Ontario Trillium Foundation has four Investment Streams: Seed, Grow, Capital and Collective Impact. A self-assessment is available on the website to find out which Investment Stream best suits your project. Each stream has it’s own criteria, applications, organization registration deadline, and the application deadline. For more information, visit http://www.otf.ca/apply-grant.

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

MICHIPICOTEN FIRST NATION MICHIPICOTEN RIVER LAKE STURGEON ASSESSMENT

MAGNETAWAN FIRST NATION LAKE STURGEON ASSESSMENT

A Lake Sturgeon spawning survey and radio telemetry study was completed in the Michipicoten River by the Anishinabek/Ontario Fisheries Resource Centre (A/OFRC), in partnership with Michipicoten First Nation, the Ministry of Natural Resources and Forestry (MNRF), Natural Resource Solutions Inc., and Brookfield Renewable Energy Partners, during the summer of 2014.

A Lake Sturgeon Spawning Assessment was completed on the Magnetawan River in 2014. The Magnetawan River is located on the eastern shore of Georgian Bay in Lake Huron and flows into the Byng Inlet. This project was funded by Magnetawan FN members lift a gill the Provincial Species at net on the Magnetawan River Risk Stewardship Fund (SARSF). Magenetawan First Nation approached the A/OFRC with concerns of the status and health of Lake Sturgeon within their traditional fishing territory. The purpose of this project is to collect baseline data on spawning activity and habitat utilization of Lake Sturgeon in the Magnetawan River.

Efforts were focused on capturing Lake Sturgeon as they moved upriver to potential spawning locations. All Lake Sturgeon captured were sampled for fork length (mm), total length (mm), girth (mm), round weight (g), species specific ageing structures, external identification of sex and maturity, internally tagged with a PIT tag and externally tagged with a white FLOY tag. If feasible, the newly captured Lake Sturgeon were equipped with a radio tag. Manual radio telemetry sweeps were utilized to detect previously radio tagged Lake Sturgeon. Field work was conducted from June 9 to July 31, 2014. This is the third consecutive year this study has been undertaken. A total of nine Lake Sturgeon have been radio tagged to date. Five radio tagged Lake Sturgeon ascended the Michipicoten River to Scott Falls Generating Station and remained there for several weeks while the water reached optimal spawning temperatures. Two radio tagged Lake Sturgeon entered the Michipicoten River and remained in the lower portion of the Michipicoten River below hiwy17 during the study period. The Michipicoten River hosts a small number of spawning individuals each year. It is evident that the Michipicoten River is utilized by a small number of Lake Sturgeon for the sole purpose of spawning. The Lake Sturgeon concentrate at the base of Scott Falls Generating Station until the water reaches optimum spawning temperature. When the spawn is finished, they move rapidly out A Michipicoten River Lake Sturgeon with a of the river, back into newly implanted radio transmitter Lake Superior.

The project began when water temperatures reached 10 oC to 12oC, which are optimal spawning temperatures for Lake Sturgeon. All Lake Sturgeon captured were sampled for fork length (mm), total length (mm), girth (mm), round weight (g), species specific ageing structures, external identification of sex and maturity, internally tagged with a PIT tag and externally tagged with a white FLOY tag. Other game fish species were fully biologically sampled. Field work was conducted from May 20 to June 6, 2014. Water temperatures ranged from 12.5oC to 19oC. A total of 40 nets were set throughout the mouth of the Magnetawan River capturing zero Lake Sturgeon. Other fish species caught and live released included Brown Bullhead, Channel Catfish, Redhorse Spc., Longnose Gar, Muskellunge, Northern Pike, Rock Bass, Smallmouth Bass, Walleye, White Sucker, and Yellow Perch. A Lake Sturgeon study by the A/OFRC in 2009 in the Magnetawan River resulted in the capture of one adult Lake Sturgeon. The 2014 Lake Sturgeon spawning assessment captured zero Lake Sturgeon. This is the third study that has confirmed that Lake Sturgeon do not likely utilize the Magnetawan River as spawning grounds.

Fish Soup

Stuffed Fish

2 lbs Whitefish

1 large Lake Trout

2 tbsp. Lard

1/2 cup diced celery

1 cup milk

1/4 cup chopped onion

1 small onion

2 tbsp. salt

2 parsley sprigs

2 tbsp. butter

2 egg yolks

2 tsp. grated lemon rind

2 tbsp. flour

1/2 tsp paprika

Wash and dry fish. Cut into two or three

pieces. Simmer in water for 1/2 hour. Melt lard and stir in flour, egg yolks,

1/3 cup sour cream 2 1/2 cups bread crumbs 2 tbsp. melted butter

parsley sprigs, onion and milk. Let boil

Wash and dry fish and sprinkle inside with

for 20 minutes. Add strained fish and let

salt. Sautee celery and onion in butter

boil until fish is tender. Serve with toast

until tender. Combine lemon rind, salt,

or crackers.

paprika, sour cream and mix with bread crumbs. Add celery and onions and toss

lightly until well blended. Stuff fish loosely and sew opening or keep together with skewers or toothpicks. Place on greased baking pan and brush with melted butter. Bake at 450°F.

A special Miigwech goes out to the Ojibway Cultural Foundation for allowing us to use recipes found in “Nishnabe Delights” by Martin Panamick. For more resources from the OCF, visit www.ojibweculture.ca/resources

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

Match the fish species with it’s name! And learn some Anishinabemowin at the same time! (Answers on page 19)

LONG LAKE #58 FIRST NATION LAKE STURGEON ASSESSMENT Two Lake Sturgeon Assessments were successfully completed on the Kenogami River system. The assessments were completed on Chipman Lake and Ogahala Lake. This study followed a Measuring the girth of a Lake Sturgeon Lake Sturgeon Index Netting (LSIN) survey protocol developed by the Ontario Ministry of Natural Resources and Forestry (MNRF) to assess Lake Sturgeon populations in river systems. The LSIN survey uses large mesh gill nets to target sub-adult and juvenile Lake Sturgeon. The extra-large mesh gill nets target mature adult Lake Sturgeon. All Lake Sturgeon and sport fish species present were sampled for fork length (mm), total length (mm), girth (mm), round weight (g), species specific ageing structures, external identification of sex and maturity, internally tagged with a PIT tag and externally tagged with a white FLOY tag. A total of 47 gill nets were set in Chipman Lake from October 15 19, 2014 capturing 327 fish from 10 different species. The most abundant species captured include Lake Herring (104), Walleye (77) and Burbot (37). A total of 3 Lake Sturgeon were captured, tagged and released in Chipman Lake. A total of 34 gill nets were set in Ogahala Lake from October 21 - 22, 2014. A total of 195 fish were caught representing 10 different species. The most abundant species captured include Walleye (70), Northern Pike (37) and White Sucker (26). Catch composition differ from that of Chipman Lake due to Ogahala Lake’s smaller size and shallower waters. A total of 12 Lake Sturgeon were captured, tagged and released in Ogahala Lake. Given the low number of captured Lake Sturgeon, this study was not able to assess population characteristics. This study also did not assess Lake Sturgeon movements or spawning areas given the limited scope of the study. In 1984, the MNRF conducted a 3 year study on Lake Sturgeon in the Kenogami River system. The 1984 study captured over 1000 Lake Sturgeon. Since then there has been few Lake Sturgeon Assessments and spawning areas are still relatively unknown on the Kenogami River System. The A/ OFRC recommends a multi-year Lake Sturgeon assessment on the Kenogami River System to provide updated information on Lake Sturgeon population characteristics and possible spawning locations.

OJIBWAYS OF GARDEN RIVER FIRST NATION LAKE STURGEON SPAWNING ASSESSMENT Year 2 of 3 of the Garden River Lake Sturgeon Spawning Assessment was successfully completed in the spring of 2014 by the Anishinabek/ Ontario Resource Centre (A/OFRC), Ojibways of Garden River First Nation and Lake Superior State University. This project was funded by the Ontario Ministry of Natural Resources and Forestry's Species at Risk Stewardship Fund. The purpose of this study was to determine Lake Sturgeon spawning grounds at Murphy's Rapids. To accommodate the shallow Garden River habitat, short largemesh gill nets were used to capture adult Lake Sturgeon. 8” and 10” mesh sizes were used, and the gill nets measured 3’ (height) by 50’ (length). D-shaped larval drift nets were set above and below the suspected Lake Sturgeon spawning grounds at Murphy's Rapids to capture larval Lake Sturgeon. A data temperature logger was placed in the river through the duration of the study to monitor hourly changes in Drift nets used to capture larval mean river Lake Sturgeon temperature. The field work took place June 2 to July 1, 2014 when water temperatures ranged from 15oC to 23oC. A total of 72 gill nets were set at the Big Bend and Murphy's Rapids producing a catch of two adult Lake Sturgeon. The drift netting effort produced a catch of 101 larval Lake Sturgeon. There were no significant difference in the size of larval Lake Sturgeon captured throughout the Garden River. Larval Lake Sturgeon were captured throughout the Garden River sampling sites. It is suspected that the main Lake Sturgeon spawning grounds is still further upriver form the Murphy's Rapids location. In 2015, the A/OFRC and Garden River First Nation will complete year 3 of 3 of the Garden River Lake Sturgeon Spawning Assessment including a Juvenile Sturgeon Assessment.

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS PAYS PLAT FIRST NATION LAKE SUPERIOR JUVENILE LAKE STURGEON SURVEY

RED ROCK INDIAN BAND NIPIGON RIVER LAKE STURGEON SPAWNING ASSESSMENT

A Juvenile Lake Sturgeon Assessment in Northeastern Lake Superior was conducted in the summer of 2014. The purpose of this study is to identify the relative abundance and distribution of juvenile Lake Sturgeon Pays Plat First Nation member Shawn within the proximity of Bouchard measuring a Lake Sturgeon the Gravel River, Pays Plat River, Steele River, Prairie River, and Little Pic River. This project is part of a larger lake wide assessment of juvenile Lake Sturgeon.

A Lake Sturgeon Spawning Study within the Nipigon River and Lake Helen was completed by the Anishinabek/ Ontario Fisheries Resource Centre (A/OFRC), Red Rock Indian Band (RRIB) and the Ministry of Natural Resources and Forestry (MNRF) in summer 2014. With the help of the MNRF, one Lake Sturgeon MNRF employees searching was fitted with a radio for Lake Sturgeon at the transmitter. A total of 10 Alexander Dam using an Lake Sturgeon are radio underwater video camera tagged in Lake Helen since the Lake Sturgeon studies began in 2008.

A Juvenile Lake Sturgeon Assessment uses standardized gear. Following the standardized protocol, a total of 16 nets are set within 5km of each river mouth. Six gill nets are to be set in 2m-5m depth stratum, six nets in the 5m-10m depth stratum, and four nets in the 10m-15m depth stratum. All Lake Sturgeon captured were sampled for fork length (mm), total length (mm), girth (mm), round weight (g), species specific ageing structures, external identification of sex and maturity, and are internally tagged with a PIT tag and externally tagged with a white FLOY tag. Two A/OFRC crews with the help of two members of Pays Plat First Nation completed the field work component between July 21 to 31, 2014 when water temperatures ranged from 4.85 oC to 13.5oC. A total of 80 nets were set capturing seven Lake Sturgeon at the Little Pic River, and six Lake Sturgeon at the Prairie River. Two previously tagged Lake Sturgeon were captured at the Prairie River. Of the two recaptures; one was from a Department of Fisheries and Oceans (DFO) study and another was tagged by the AOFRC from a previous study. This project provided valuable information on the importance of the area surrounding the Prairie River and Little Pic River area of Lake Superior for juvenile Lake Sturgeon. This study confirmed that the area around the Gravel River yields no catch of juvenile Lake Sturgeon. This project was considered a success due to the capture of 15 juvenile Lake Sturgeon and recapturing 2 previously tagged individuals. The success in capturing juvenile Lake Sturgeon in this area stresses the importance of suitable foraging habitat and that Lake Sturgeon will travel great distances when in a lake environment.

Captured Lake Sturgeon were biologically sampled which included measuring fork length (mm), total length (mm), girth (mm), weight (g), and external identification of sex. Lake Sturgeon were tagged externally with a FLOY tag, as well as equipped with a radio transmitter. In total, 115 net sets were completed from June 26 to July 27, 2014 yielding two untagged Lake Sturgeon and two recaptures from previous years. Telemetry of previously tagged Lake Sturgeon took place throughout this study. Two Lake Sturgeon were detected in the river on June 27, 2014 when water temperatures reached 9.8°C. By manually sweeping the spawning areas at Alexander Falls, the MNRF was able to video record and identify new and previously untagged Lake Sturgeon. Temperatures within the Nipigon River at this time were 13.0°C. A total of four Lake Sturgeon were captured in the 2014 Lake Sturgeon Assessment in the lower Nipigon River and Lake Helen. Of these four captured, one Lake Sturgeon was a recapture from the 2012 Lake Sturgeon Study, and one originated from a study conducted by an environmental services group for a neighbouring community. The 2014 Lake Sturgeon Study resulted in the capture of two new Lake Sturgeon. In total, 14 Lake Sturgeon have been captured, tagged and released by the A/OFRC and RRIB since 2008. This information will help RRIB in managing and protecting areas which may be critical to the rehabilitation efforts of this particular Lake Sturgeon population.

• WHAT TO DO • WHO TO CALL • WHAT INFORMATION IS REQUIRED

Why tag fish? Tagging is a biological method for monitoring fish and assessing populations. The reason for doing this is to tell one fish from another so its daily movements or seasonal migrations can be studies and rates of growth can be learned. Tags have a unique number printed on them, along with a phone number to call to report that the caught tagged fish. When a fish is first tagged, basic information, such as when and where it was tagged and its size at release, is recorded with its tag number. When the fish is recaptured, biologists can use the tag number to match up the release information with the recapture information and learn how long the fish was at large, how far the fish travelled, and how much it grew during that time period. Tagging is an important tool for monitoring fish because they spend their entire lives out of the sight of researchers trying to learn about them. With enough tagging data, fisheries biologists could estimate fish migratory behaviour, population structures, and mortality rates.

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

SAGAMOK ANISHNAWBEK NORTHERN PIKE SPAWNING ASSESSMENT PIC MOBERT FIRST NATION WHITE LAKE CREELSURVEY The Anishinabek/Ontario Fisheries Resource Centre, in partnership with Pic Mobert First Nation, completed a recreational angling creel survey on White Lake throughout the 2014 open-water angling season. The objectives of this study were two-fold; 1) Compliment the data gathered in the 2013 FWIN conducted by the A/OFRC on White Lake. 2) Monitor fishing efforts on the lake, particularly on the walleye population, to gain a better understanding of the catch and harvest of sportfish. Crews circulated White Lake to estimate the number of boats and anglers that were present and conducted interviews with anglers to estimate harvest amounts and characterize angling behaviour. These surveys were conducted on 17 separate occasions between June 14 and September 29, 2014 including nine weekend days and seven weekdays. As part of these interviews, anglers were asked questions to determine their origin, the duration and frequency of their fishing trips, fishing methods and species targeted, and the number of fish harvested and/or released. The location where anglers were fishing along with biological data on catches were also recorded. Field crews conducted 41 angler counts which represented a total of 99 individual anglers. Walleye was the most sought after species and catch rates reflected this. Walleye made up 74% of the total catch, Yellow Perch made up 16% of the catch and Northern Pike made up 10% of the catch. 95 Walleye were retained for consumption. 66% of the anglers were local while 24% and 10% were from Ontario and the USA, respectively. Troll fishing was the most popular form of angling on the lake. The results from the creel survey have given insight into angler fishing habits, fishing gear used and species preferred for capture and retainment. Further studies will continue to monitor fishing pressure through continual creel surveys and/or access surveys to better determine the magnitude of fishing pressure on White Lake.

MISSISSAUGA #8 FIRST NATION CHIBLOW LAKE CREEL SURVEY AND SUMMER PROFUNDAL INDEX NETTING A Summer Profundal Index Netting (SPIN) survey was conducted by the A/OFRC in partnership with Mississauga First Nation on Chiblow Lake in the summer of 2014. The SPIN was paired with a creel survey to attempt to assess the health of the lake trout population and current pressure on the fishery. The study was conducted between July 14—16, 2014 and a total of 42 nets were set. Gill nets were 64 m in length and consisted of panels 8 m in length with varying mesh sizes (57, 64, 70, 76, 89, 102, 114 and 127 mm). Gill nets were set for two hour intervals to reduce the amount of fish kill. Gill nets were set in randomly selected locations within six different depth strata (0–10, 10-20, 2030, 30-40, 40-60 and 60–80 m). Species of interest, lake trout and lake whitefish, were fully sampled for ageing samples, length and weight. All other species were sampled for length and live released. The creel survey was conducted from July 14 through September 1, 2014 and a grand total of 258 anglers were interviewed. A total of 223 fish were captured throughout the study, representing four different species. The overall catch per unit effort (CPUE), for all species combined, was 6.13 fish/net/day and the most dominant species was Lake Whitefish (comprising of 69.51% of the total catch). A total of 36 Lake Trout were captured in the course of the study. The lake trout catch rate of anglers was low, but often resulted in the fish being harvested (~90% harvest rate). The fish that was caught most often were smallmouth bass (comprising ~76% catch rate). There is a population of Lake Trout in Chiblow Lake that seems to be receiving some angling pressure. High harvest rates may lead to this population becoming unsustainable if fishing pressure increases.

The Anishinabek/ Ontario Fisheries Resource Centre (A/OFRC) successfully completed the second consecutive year assessing Northern Pike spawning in Sagamok Anishnawbek traditional territory in the spring of 2014. The netting survey took place in four main bays: the Pow Wow Grounds, A/OFRC Fisheries Technician John’s Bay, Perch Bay, and Oak processing a small Northern Pike Bay. caught in John’s Bay This Northern Pike Spawning Study used 6’ trap nets as a live-catch -sample-release method. Trap nets were set overnight and retrieved every morning. All Northern Pike and sport fish species that were present were sampled for fork length (mm), total length (mm), round weight (g), species specific ageing structures, external identification of sex and maturity, and were externally tagged with a white FLOY tag. Non-target fish species were enumerated by size class based on their fork length (mm) and were live released. A total of 612 fish were captured throughout the study, representing 13 different species. 84 Northern Pike were captured during the 2014 study, 74 of which were equipped with an external FLOY tag. A total of 103 Northern Pike have been tagged since 2013. There were no recaptures from previous years during the 2014 study. One tagged Northern Pike from the 2014 project was recovered on July 21, 2014. The Northern Pike with the FLOY tag 2082 was tagged in John’s Bay on May 6, 2014, and its capture location was approximately 12 km away in Oak Bay. A total 84 of Northern Pike were caught in the waters of Sagamok Anishnawbek in 2014, with a total of 141 Northern Pike caught since 2013. 74 Northern Pike were equipped with a FLOY tag in 2014, resulting in 103 North Pike being tagged since 2013. This was year 2 of a 3 year study. The final portion of this project will be undertaken in the spring of 2015. By sampling for multiple and consecutive years, the likelihood of unique weather conditions impacting the overall results is decreased. Future studies will also employ the use of fyke nets in the channels and areas around the current study sites to obtain accurate representation of Northern Pike spawning and migration.

OJIBWAYS OF THE PIC RIVER FIRST NATION KILLALA LAKE SUMMER PROFUNDAL INDEX NETTING A Summer Profundal Index Netting (SPIN) survey was conducted from July 22 to July 28, 2014. The objective of this study is to estimate the abundance and status of Lake Trout in Killala Lake, which serves as an important lake for egg collections by the Ministry of Natural Resource’s Lake Trout stocking program. Killala Lake is identified as a Lake Trout sanctuary situated in both the Ojibways of the Pic Rivers traditional territory and in the Killala Lake Conservation Reserve. The 2014 SPIN follows a set of standardized methodologies in order to achieve two objectives: first, to estimate the density of harvestable sized Lake Trout in the lake; and secondly, to attain a representative sample of the adult Lake Trout population across the range of lake depth and area. The latter is used to evaluate the biological integrity of the population and to monitor for effects on the Lake Trout population. A total of 114 fish were captured throughout the study including 53 Lake Trout. The largest Lake Trout captured weighed 5.3 kg (11.7 lbs.) and was 78.8 cm (31”) in length. In addition to Lake Trout, a Lake Trout captured in Killala Lake total of 53 Lake Whitefish were also captured during the study with the largest being 2.2 kg (4.8 lbs.). Fish captures were higher in the lower basin of Killala Lake, however the fish were slightly larger in the upper basin of Killala Lake. The average Lake Trout Length and weight was 530.7mm and 1714.5g, respectively. A total of 7 year classes were captured during the study. The average age was 8.4 years and the ages ranged from 4 years to 21 years. The Lake Trout in Killala Lake are of the large-bodied type. Their diet consists mainly of fish, and they are fast growing until the age of 10 years. They mature late (approximately 8 years), and live up to 20+ years, which is considered long lived. Killala Lake itself provides optimal habitat for the resident Lake Trout population, as it provides deep, clear waters that are rich in oxygen. Dissolved oxygen levels in July 2014 ranged from 9.91 mg/L to 7.19 mg/l. Overall, this population is considered healthy and stable given that abiotic and biotic conditions remain stable. This study has assisted the Ojibways of the Pic River by gathering baseline information on the Lake Trout population residing in Killala Lake. Future monitoring of this sensitive indictor species within Killala Lake will assist in identifying changes in the lakes ecosystem as well as changes in the land which surrounds the Lake.

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

2014/2015 FIELD PROJECTS WHITEFISH RIVER FIRST NATION MCGREGOR BAY END OF SPRING TRAPNETTING The second half of the Early Summer Trap Netting (ESTN) project in McGregor Bay was successfully completed in the spring 2014. The purpose of this project is to gather information on Walleye species in McGregor Bay and to evaluate the success of the Upper Great Lakes Management Units (UGLMU) Walleye stocking efforts. Information gathered will assist in the management of the Walleye resource in McGregor Bay.

ALDERVILLE FIRST NATION ONTARIO STREAM ASSESSMENT PROTOCOL A stream assessment was completed on Dowler Creek, No Name Creek, and Southside Creek. The project took place from September 16th to September 18th, 2014. Following the methodologies outlined in the Ontario Stream A/OFRC field staff doing some Assessment Protocol (OSAP), four electrofishing on Dowler Creek. sites were identified. Channel morphology was recorded for two sites, while fish and benthic invertebrate communities were sampled for three sites. From all sites, water samples were taken and sent to the Ministry of the Environment and Climate Change to be analysed for nitrate, nitrite, phosphates and pH. Benthic macroinvertebrates were sampled in two riffles and one pool for all three streams. The first sampling site on Dowler Creek will be compared to a past electrofishing study completed at the same location in 2007. A total of 16 Brook Trout were sampled and released in 2014 compared to 14 Brook Trout captured in 2007. Other fish species captured include Blacknose Dace and Northern Pearl Dace. A second site on Dowler Creek was identified and a water sample was taken, but there was not time to sample fish and benthic invertebrates. No Name Creek is another tributary to Rice Lake and provides cold water habitat for Brook Trout. Fish species captured and released include Brook Trout, Creek Chub, Blacknose Dace, and Northern Pearl Dace. Water temperatures were at 10.3°C and pH was 8.33. Southside Creek is another tributary to Rice Lake that runs through wetlands prior to the sample site. Southside Creek had a larger variety of fish species present: Blacknose Dace, Creek Chub, Common White Suckers, and Brook Stickleback. This project provided valuable insight into the fish community and the habitat where they reside. Water samples taken will be analyzed and included in the detailed technical report.

ATIKAMEKSHENG ANISHNAWBEK ROUND LAKE ENVIRONMENTAL EFFECTS MONITORING & LONG LAKE ONTARIO STREAM ASSESSMENT PROTOCOL The Environmental Effects Monitoring (EEM) was completed in Round Lake on October 20, 2014. This study was designed to determine any effects to fish populations in Round Lake from the Long Lake Gold Mine. The Long Lake Gold Mine tailings resulted in contamination of the surrounding environment with heavy metals. The mine and tailings ponds are located approximately 4km east of Round Lake. Two FWIN (Fall Walleye Index Netting) nets and three small mesh BSM (Broadscale Monitoring) nets were set to capture fish. Nets were set for approximately 24 hours.

An ESTN follows the Ministry of Natural Resources and Forestry (MNRF) protocol. ESTN protocol requires two consecutive years of sampling and uses live-catch-and-release methods. All captured Walleye and game fish species were biologically sampled. This included measuring length and weight, collecting an ageing structure, noting fin clips, and applying an internal and external tag. All other fish species were measured for length and were live released. McGregor Bay Walleye. Field work was completed from May 20 to 28, 2014 when water temperatures ranged from o o 12 C to 17 C. In 2014, a total of 348 fish were captured comprising of 14 different species. 10 Walleye were captured and 40% had fin clips indicating a stocked origin. In 2013, the A/OFRC conducted an ESTN and Walleye Tagging Study that captured 31 Walleye, and 68% of these had fin clips. Over two years (2013-14) the A/OFRC captured a total of 41 Walleye in McGregor Bay. It is evident that the Walleye abundance and age structure improved from 1998 to 2007 as a result of the stocking program. However, the Walleye population now largely consists of stocked individuals. All Walleye were equipped with an external FLOY tag with contact information. These fish provide crucial information on the Walleye population in McGregor Bay. All people are encouraged to report any caught tagged fish.

A total of 32 fish comprising of three species were captured and sampled. Fish catch was as follows: Rainbow Smelt (29), Northern Pike (2), and Cisco (1). All fish caught were biologically sampled and sent for contaminant analysis. Long Lake creek was unable to be sampled with the Ontario Steam Assessment Protocol (OSAP). A/OFRC is awaiting results from the Ministry of Environment and Climate Change contaminant lab.

Round Lake and Long Lake. Orange box indicates tailings ponds

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Fish scales are sometimes used in lipstick!

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Walleye have night vision! Which makes perfect sense, as they prefer murky waters. They have marble-like eyes which let them see well in dim light. Their retinas have a layer of reflective pigment that intensifies any light that the eye receives.



Researchers studying walleye vision have found that orange is the colour most visible to walleye, followed by yellow and yellow-green. A great tip to remember when choosing your tackle!

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The best time to catch walleye is five to seven weeks after the fish have completed spawning. At this time, the females have not eaten in nearly two months, and they’re hungry for anything they can find!

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Why is it that pike and musky’s can easily shear your fishing line, which an equally toothy walleye rarely do? It turns out that walleye teeth are round, which pike and musky have razor sharp edges. I still wouldn’t recommend sticking your finger in a walleye’s mouth. (Sternberg, Dick.2009. 50 Fishy Facts. <http://www.outdoorlife.com/node/1005007957?page=0%2C4>)

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

2014/2015 FIELD PROJECTS CHIPPEWAS OF KETTLE & STONY POINT FIRST NATION ONTARIO STREAM ASSESSMENT PROTOCOL

MAGNETAWAN FIRST NATION WALLEYE SPAWNING AND REHABILITATION WORKSHOP A Walleye Spawning Survey and End of Spring Trap Netting (ESTN) survey was conducted in the Magnetawan River in 2014. The objective of these projects are to evaluate the population status of spawning Walleye and to identify rehabilitation options that could be implemented to enhance the number of Walleye species in the Magnetawan River system. Nets were set and checked at 2 hour intervals to reduce fish kill. The A/OFRC follows the ESTN’s live catch sample release protocol created by the Ontario Ministry of Natural Resources and Forestry. ESTN are conducted in the spring when water temperatures reach 12oC. The spawning survey component of this study took place from April 28 to May 16, 2014 when water temperatures ranged from 3°C to 12°C. A total of 25 Walleye were captured, tagged, and live released from these gill nets. The ESTN survey was completed between May 19—30, 2014 when water temperatures ranged from 13 oC to 19oC. A total of three Walleye were captured during this survey and none had previously been tagged. Other fish species captured during these two surveys included Northern Pike, Redhorse, Pumpkinseed, Bowfin, White Sucker, Brown Bullhead, Rock Bass, Black Crappie, Channel Catfish, and Longnose Gar. In addition to assessing the Walleye population, two Magnetawan First Nation crew members were trained in and acquainted with fisheries monitoring techniques and rehabilitation options. Using the information from this project and the experience of these crew members, Magnetawan First Nation can begin to assess the feasibility of various rehabilitation options that will enhance the number of Walleye in the Magnetawan A nice Walleye that has been equipped River system. with a FLOY tag

NAMAYGOOSISAGGUN FIRST NATION SHAWANABIS LAKE FALL WALLEYE INDEX NETTING A Fall Walleye Index Netting (FWIN) survey was completed on Shawanabis Lake in the fall of 2014. A previous FWIN Survey was conducted on Shawanabis Lake in 2003. Results from the 2014 FWIN will be compared to the 2003 A/OFRC Fisheries Intern untangles a data to identify changes in Walleye from a FWIN net the Walleye population. The information will be scored against provincial Walleye benchmarks. A FWIN follows a standard protocol developed by the Ontario Ministry of Natural Resources and Forestry (MNRF) to monitor Walleye populations. A FWIN consists of setting gill nets overnight when water temperatures range between 10oC—15oC in the fall. All Walleye and other sport fish captured were fully biologically sampled which included measuring lengths and weight, identifying sex and maturity, and collecting ageing structures.

A stream assessment on Shashawanda Creek was completed from September 18 to September 21, 2014. The stream assessment consists of documenting physical habitat, benthic macroinvertebrate samples and fish communities by following the methodologies outlined in the Ontario Stream Assessment Protocol (OSAP). Water samples were taken and sent to the Ministry of the Environment and Climate Change to be analysed for nitrate, nitrite, phosphates and pH. Benthic macroinvertebrates were sampled in two riffles and one pool for all three sites. Fish community was sampled using the electrofishing technique, where fish are sampled and live released. Due to the southern climate, there was a diverse fish community including Northern Pike, Common Shiner, White Sucker, Creek Chub, Blacknose Shiner, Rainbow Darter, Pumpkinseed, Johnny Darter, Blackside Darter, Iowa Darter, Rock Bass, Bowfin, Largemouth Bass, Rock Bass and Common Carp. This study has provided valuable information regarding fish community composition, stream morphology, and water chemistry. With this information, Chippewas of Kettle and Stony Point First Nation will gain insight into the health and quality of their water sources, and assist in identifying contaminant sources.

In 2014, a total of 24 nets were set producing 405 fish that represented 11 different species. Walleye had the highest catch with a total of 236 captured. Other species captured include Burbot, Cisco, White Sucker, Lake Trout, Lake Whitefish, Longnose Sucker, Northern Pike, Shorthead Redhorse, Trout-perch, and Yellow Perch. In 2003, a total of 28 nets were set producing 314 fish representing 10 different species. A total of 239 Walleye were captured during that project. The Walleye population in Shawanabis Lake appears to be healthy when compared to the provincial benchmarks. Another FWIN should be done in 5 years time to monitor any changes to the Walleye population.

WAHNAPITAE FIRST NATION ONTARIO STREAM ASSESSMENT PROTOCOL A stream assessment was conducted on Mountain Creek from September 29th to October 2nd, 2014. Following the methodologies outlined in the Ontario Stream Assessment Protocol (OSAP), sites were identified and described, channel morphology and physical A/OFRC Fisheries Technician features were recorded, and conducts stream morphology on a fish and benthic invertebrate section of creek communities were sampled. This data will allow Mountain Creek to be compared to other streams in the provincial database. The A/OFRC will draw conclusions on the health of the streams ecosystem by analysing the data collected (i.e. water quality and species present). The two sample sites were located on Portelance Road, at a location where Mountain Creek flows into Lake Wahnapitae. Fish species sampled include: Pumpkinseed, Longnose Dace, Creek Chub, Northern Pearl Dace, Common Shiner, and Black Chin Shiner. Water levels were high and fast flowing at both sites. Physical stream features were recorded at 10 transects for each site—this included stream bank width, terrestrial vegetation, aquatic vegetation, depth, flow, substrate, and cover. Benthic invertebrates samples included Stoneflies, Caddisflies, and Mayflies. These are important insects, and are used as indicator species of water quality. Water samples were taken and sent to the Ministry of the Environment and Climate Change to be analysed for nitrate, nitrite, phosphates and PH. Changes in the biotic and physical quality of Mountain Creek can be monitored at the established sampling sites. The information gathered during this project will assist in identifying potential contamination sources and provide baseline data to Fish collected using a backpack compare with future water projects with electrofisher quality Wahnapitae First Nation.

A/OFRC Staff measure and weigh fish caught while electrofishing.

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

2014/2015 FIELD PROJECTS MICHIPICOTEN FIRST NATION LAKE SUPERIOR FISH COMMUNITY INDEX NETTING A Fish Community Index Netting (FCIN) survey was conducted in Michipicoten Bay on Lake Superior in the summer of 2014. This is the first FCIN conducted by the A/OFRC in the area. This study will gather baseline fish information to be used for comparison in future projects.

CHIPPEWAS OF GEORGINA ISLAND NEARSHORE SMALL FISH BIODIVERSITY A Nearshore Small Fish Community Assessment was conducted in Lake Simcoe around Georgina Island, Snake Island, and Fox Island during the summer of 2014. The purpose of this study was to examine changes in fish biodiversity compared to previous studies conducted in 1996 and 2008. This project was funded by the Environment Canada’s Lake Simcoe/South-eastern Georgian Bay Clean-Up Fund. The nearshore small fish community was assessed by seine netting and setting small mesh gill nets. Small mesh gill nets were set overnight in shallow water and a single seine net haul was conducted in the daytime for each site. There were 5 sites located on Snake Island, 4 sites on Fox Chippewas of Georgina Island First Island and 24 sites on Nation member Dakota Wyld Georgina Island. All fish were conducts a seine net pull identified to the species level in the field and were live released. This project began July 1, 2014 and continued until August 30, 2014 with water temperatures ranging from 17°C to 25°C during this time. A total of 17 species were captured during this study. The most commonly encountered fish species were Round Goby (Neogobius melanostomus), Emerald Shiners (Notropis atherinoides) and Yellow Perch (Perca flavescens). Small fish make up a large part of Lake Simcoe’s biodiversity and play a role in the lake’s ecosystem. This study shows that there have been shifts in the Lake Simcoe fish community for Georgina Island, Fox Island, and Snake Island since 1996. This shift in nearshore fish community coincides with other changes to the Lake Simcoe ecosystem. Examples include introduced species such as Dreissenid mussels, Quagga mussels, Eurasian Water milfoil, Round Goby, Rusty Crayfish, as well as changes in water quality and habitat.

SHESHEGWANING FIRST NATION BAYFIELD SOUND NEARSHORE COMMUNITY INDEX NETTING A Nearshore Community Index Netting (NSCIN) project was completed in the summer of 2014. The project study area included the Sheshegwaning First Nation (SFN) shoreline and extended into Bayfield Sound on Lake Huron.

A/OFRC Fisheries Intern Lucas Beaver holds up a large Walleye caught in Bayfield Sound

A NSCIN project follows the protocol established by the Ontario Ministry of Natural Resources and Forestry (MNRF). Trap nets were set for a 24-hour period, at which point they were lifted, analyzed, and re-located. A total of 29 trap nets were set during the project. All captured game fish species were biologically sampled. This included measuring length and weight, collecting an ageing structure, and noting any fin clips and external tags. All other fish species were measured for length and released.

FCIN is a survey method that is designed to target the off shore fish community and gather information on fish population characteristics and abundance. Nets were set in four depth strata; 0-30m, 30-60m, 60-90m, and >90m. All nets were set in Michipicoten Bay on Lake Superior within a 25 km radius of the Michipicoten River mouth. All captured game fish species were fully biologically sampled, which included measuring length and weight, collecting an ageing structure, and noting fin clips and external tags. All other fish species were measured for fork length and released. Field work was conducted between August 13 - 20, 2014 in Lake Superior when water temperatures ranged between 6 oC and 8oC. 20 nets were set and a total of 748 fish were captured representing 8 different species. Fish species captured included Lake Trout, Lake Whitefish, Longnose Sucker, Herring, Round Whitefish, Bloater, Burbot, and White Sucker. This project was successful in gathering baseline fish information on Lake Trout and Lake Whitefish for Michipicoten First Nation. Another FCIN study should be done in 2018 or 2019 to monitor changes in the fish community.

Field work was completed from August 25 to September 5, 2014. Water temperatures ranged from 14oC to 21oC. A total of 145 fish representing nine species were captured. Smallmouth Bass, 93 captured, was the dominant species representing 64% of the total catch. Other species caught included; Rock Bass, White Sucker, Walleye, Rainbow Trout, Northern Pike, Pumpkinseed, Common Carp, and Bowfin. Nearshore habitat was also recorded while at netting sites. The catch dominated by Smallmouth Bass is attributed to little variety in shoreline features between sites. Due to the type of netting project, the time of year, and the limited nearshore habitat, the catch was expected to be fairly low when compared to other netting projects. A different netting method is recommended for future studies. Beautiful Lake Superior

WASAUKSING FIRST NATION THREE MILE HABITAT SURVEY The first habitat assessment for Three Mile Lake, located on Parry Island was took place from August 12-15, 2014. Littoral and shoreline substrate and vegetation along multiple shorelines were surveyed by boat. In total, approximately 18km of littoral zone and shoreline were surveyed. In addition to habitat surveying, the A/ OFRC crew also obtained data for a bathymetric map for Three Mile Lake and deployed multiple minnow traps and two lake survey gill nets. Fish species encountered during the netting portion of this project included Northern Pike, Smallmouth Bass, Brown Bullhead, Yellow Perch, Rock Bass, Pumpkinseed, and Blacknose Shiner. Two Northern Pike captured were infected with black spot disease. It should be noted that although unsightly, fish infected with black spot disease are perfectly safe to eat as long as it is cooked properly. Some aquatic plant species observed during the survey include Yellow Pond Lily, Fragrant White Water Lily, Floating Leaved Burreed, Water Shield, Hard-stem Bulrush, Common Cattail, Pickerelweed, and various pondweed species. This project has provided good baseline data for future studies which will be conducted on Three Mile Lake. Through this study we have identified critical habitat which support sport fish, as well as identify potential areas of Shoreline typical of Three Mile Lake interest. This data, along with the data from a 2015 Broad Scale Monitoring project which will be taking place on Three Mile Lake, will greatly aid Wasauksing First Nation in developing a Fisheries Management Plan.

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

A/OFRC Fisheries Intern Lucas Beaver holds up a large Walleye caught in Bayfield Sound

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

2014/2015 FIELD PROJECTS CHIPPEWAS OF KETTLE & STONY POINT FIRST NATION ONTARIO STREAM ASSESSMENT PROTOCOL

A/OFRC Staff measure and weigh fish caught while electrofishing.

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

Round Lake and Long Lake. Orange box indicates tailings ponds

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Fish scales are sometimes used in lipstick!



Researchers studying walleye vision have found that orange is the colour most visible to walleye, followed by yellow and yellow-green. A great tip to remember when choosing your tackle!



Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS PAYS PLAT FIRST NATION LAKE SUPERIOR JUVENILE LAKE STURGEON SURVEY

RED ROCK INDIAN BAND NIPIGON RIVER LAKE STURGEON SPAWNING ASSESSMENT

• WHAT TO DO • WHO TO CALL • WHAT INFORMATION IS REQUIRED

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

Match the fish species with it’s name! And learn some Anishinabemowin at the same time! (Answers on page 19)

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

2014/2015 FIELD PROJECTS

MICHIPICOTEN FIRST NATION MICHIPICOTEN RIVER LAKE STURGEON ASSESSMENT

MAGNETAWAN FIRST NATION LAKE STURGEON ASSESSMENT

Fish Soup

Stuffed Fish

2 lbs Whitefish

1 large Lake Trout

2 tbsp. Lard

1/2 cup diced celery

1 cup milk

1/4 cup chopped onion

1 small onion

2 tbsp. salt

2 parsley sprigs

2 tbsp. butter

2 egg yolks

2 tsp. grated lemon rind

2 tbsp. flour

1/2 tsp paprika

Wash and dry fish. Cut into two or three

pieces. Simmer in water for 1/2 hour. Melt lard and stir in flour, egg yolks,

1/3 cup sour cream 2 1/2 cups bread crumbs 2 tbsp. melted butter

parsley sprigs, onion and milk. Let boil

Wash and dry fish and sprinkle inside with

for 20 minutes. Add strained fish and let

salt. Sautee celery and onion in butter

boil until fish is tender. Serve with toast

until tender. Combine lemon rind, salt,

or crackers.

paprika, sour cream and mix with bread crumbs. Add celery and onions and toss

lightly until well blended. Stuff fish loosely and sew opening or keep together with skewers or toothpicks. Place on greased baking pan and brush with melted butter. Bake at 450°F.

Anishinabek/Ontario Fisheries Resource Centre’s Fisheries E-Newsletter Winter 2016

Nation. We continue to serve that purpose for the 39 First Nations communities of the Anishinabek Nation. There is no shortage of demand for what we do. Every year we receive

more requests for work than our resources allow us to deliver. It’s a difficult matter to decide which communities have their projects

A/OFRC Chairperson

approved and which do not. In addition to assessing projects on

Cliff Meness, Algonquins of Pikwakanagan

each region is receiving support, whether a community has had a

OMNRF Appointments

project approved recently, whether a project is relevant to more than

Sue Chiblow, Secretary/Treasurer

one community and generally strives to treat all communities in a fair

Frank Kennedy, Retired Director of the Science and Information Branch, OMNRF Kevin Reid, Fisheries Scientist for the Ontario Commercial Fisheries Association Tom Whillans, Assoc. Professor, Environmental and Resource Studies, Trent University

and balanced manner that addresses their needs in a timely fashion. We have learned a few things over the years about getting the work done and are proud of our record of successfully completing challenging projects. We are also proud of the many people who have gained valuable experience working on our crews either as participants in our internship programs or as seasonal staff. The projects described in this newsletter are examples of our work; there are many kinds of things we can do in your community to assist with managing your fishery or informing your other initiatives with assessments of fish populations and habitat. We look forward to working with you.

Peter Meisenheimer

Anishinabek Nation Appointments Rick Stevens, Nipissing First Nation Vacant Board Positions: - Southwest Region - Southeast Region - Superior Region

For More Information CONTACT: Anishinabek/Ontario Fisheries Resource Centre 755 Wallace Road, Unit 5 North Bay, ON P1A 0E7 Phone: (705) 472-7888 Fax: (705) 472-6333 aofrc@aofrc.org www.aofrc.org

Answers to Fish Mix & Match 1F; 2C; 3A; 4B; 5D; 6G; 7E

technical merits, we use a process that takes into account whether

Baamaapii Kawaabmin!

Brought to you by: The Anishinabek/Ontario Fisheries Resource Centre