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- Ron Wierenga
- Clark County Public Works
- Water Resources Program
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- Background on Clark County Volunteer Monitoring
- Lake Problems/Lake Assessment
- Volunteer Monitoring in Vancouver Lake
- Summary of Results
- What’s Next?
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- What is it and how do we do it?
- Why monitor using volunteers?
- Summary of volunteer monitoring projects
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- A Clark County Department of Public Works, Water Resources Program
project:
- Run by Water Resources Program staff.
- Accountability is to the Clark County Board of County Commissioners and
the citizens of Clark County.
- Funding provided by the Clark County Clean Water Program and Washington
Department of Ecology Grant(s).
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- How does volunteer monitoring work?
- Need Volunteers - Clark County Watershed Stewards, citizens, civic
groups, company/corporations, schools.
- Need Support - County staff provide 1) standardized volunteer stream
and lake monitoring protocols; 2) equipment from the Clark County
Volunteer Monitoring Resource Center; 3) coordination of sampling
dates.
- Need a way to share information - Clark County’s Water Quality
Information Database.
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- Where to collect information?
- Lake sites where people recreate.
- Locations representative of overall lake conditions or of specific
conditions of study, e.g. beaches for the Health Department.
- In general, sites selected by county staff where data gaps exist.
- Locations where volunteers are interested or concerned about water
quality.
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- Why monitor with volunteers?
- Facilitate grassroots participation and education in water resource
protection.
- Collect and report credible baseline data to describe current condition
of streams and lakes.
- Add to the network of Clark County Water Resources Program monitoring
sites.
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- Summer 2002 trained volunteers to participate in the Great North
American Secchi Dip-in.
- Fall 2002 initiated program to routinely monitor four stream sites
countywide.
- Summer 2003 started monitoring Vancouver Lake with a single volunteer.
- Spring 2004 initiated Gibbons Creek monitoring project.
- Summer 2004 continued monitoring Vancouver Lake with team of volunteers.
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- “Water quality…is a term used to describe the condition of a water body
in relation to human needs or values. Quality is not an absolute; the
terms “good” or “poor” water quality only have meaning relative to the
use of the water and the attitude of the user. An oligotrophic lake
might have good water quality for swimming but be considered poor water
quality for bass fishing”,
- Robert Carlson, Kent State University
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- Depends on the lake!
- Shallow v. Deep Lakes
- Climate – tropical, temperate, elevation
- Primary uses – drinking water, recreation, wildlife
- Lake standards
- State Water Quality Rules – Mostly narrative statements like “No toxic
substances above toxic levels” etc.
- State Lake Nutrient Criteria proposed in 2003 rules
- EPA Criteria – recommendations for healthy aquatic systems
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- Lake Problems:
- Excess algae – unsightly algal blooms restricts uses.
- Excess attached plants – dense growth restricts uses.
- Exotic species – reduce native species restricts uses.
- Shallow water depth – restricts boating and swimming.
- Turbid water – reduces aesthetic values; causes food chain disruptions.
- Toxins – restricts fish consumption.
- Fecal coliform, pathogenic bacteria, and enteric viruses – causes
illness, infections, rashes.
- Undesirable fishery – increases turbidity and nutrients.
- User conflicts – restricts boating and swimming
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- Water Quality Survey – lake assessment and nutrient budgets.
- Algae Survey – amount and type of phytoplankton; presence of
bloom-forming or toxin producers.
- Aquatic Plant Survey – location and density; presence of non-native or
invasive types.
- Fish Survey – Numbers, types, and distribution; non-native species.
- Sediment Assessment – areal distribution and thickness, contaminants.
- Bathymetry and Modeling – detailed information about the lake bottom;
models describe where water comes from and goes to.
- Recreational Use Assessment –types of recreation, types of development
on the shoreline, user perceptions of the resource and potential
problems, user conflicts.
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- Gather background information including historical data
- Identify data gaps
- Evaluate potential or typical lake problems
- Typical Lake ‘Check-up’
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- 2003 trophic state determination project
- Student performed July-November monthly sampling of physical, chemical,
and algae.
- 2004 routine main-lake station monitoring by the county’s Dragonfly team
- June-October bi-monthly sampling physical, chemical, and algae.
- 2004 flushing channel inflow monitoring
- Student performed periodic sampling in and around flushing channel in
the lake.
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- Temperature – The lake is too large and shallow to stratify; vertical
gradients confined brief periods confined to calm weather; warm.
- Oxygen - Usually at acceptable levels but occasionally depleted during
periods of calm weather; “supersaturated” during algal blooms.
- pH- Very high at times due to heavy growth of algae.
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- Average Phosphorus = 0.267 mg/L; Nitrogen = 2.255 mg/L
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- Algae – excessive growth of algae restricts recreational use; potential
toxin producers dominate during the late summer.
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- Trophic State refers to the degree to which nutrients affect the algal
productivity of the lake.
- Overall TSI for 2004 was about 74 or Hyper-Eutrophic, meaning nuisance
plants, algal scums, and low transparency may discourage swimming and
boating.
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- Bacteria and pathogens – safe swimming at Vancouver Lake Park
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- Are things worse than they used to be?
- Average annual values for parameters.
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- Are things worse than they used to be?
- Average annual values for parameters.
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- Are things worse than they used to be?
- TSI based on level of Chlorophyll; 1995 data limited dataset from WA
Department of Ecology.
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