Webster Lake Plant Survey 2012 Ken Wagner, Ph.D., CLM and Maxine Verteramo Water Resource Services, Inc.

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Presentation transcript:

Webster Lake Plant Survey 2012 Ken Wagner, Ph.D., CLM and Maxine Verteramo Water Resource Services, Inc.

Plant Data 11 of 40 species dominant in 2003; not fanwort

Rooted Aquatic Plants 2003 survey of 84 points summarized into biomass ratings (also did cover). Provides impression of nuisance potential

Plants in 2003 Distribution of plants in 2003 includes sparse to no plants (blue), moderate density (yellowish), dense (orangish) and very dense (reddish) areas Largely in coves and along shore

2008 treatment By 2008, had established treatment areas to be considered on annual basis. Also have no treatment (habitat) areas

2009 Treatment Annual program includes Reward (diquat) and Sonar (fluridone) herbicide applications and physical controls such as hydroraking. Treatment based on need and budget

2010 Treatment Same approach as in 2008, but some differences in areas treated

2012 Treatments

2011 Plant Related Conclusions The lake is too large to do a thorough plant survey every year; area targeted surveys inform treatment decisions, but don’t facilitate quantitative evaluation of results It appears that plant nuisances have been reduced, but are not eliminated Eurasian watermilfoil is now non-dominant, but fanwort has risen in dominance over 8 years; variable watermilfoil continues as a dominant invasive species A once-per-decade thorough survey might allow assessment of longer term trends

2012 Survey 584 points 4 depth intervals 1 point per acre All points <10 ft deep surveyed ½ points ft deep 1/3 points ft deep

Plant Types 35 species in species in species total Some ID issues Some relative abundance changes Only about 8-12 common species

Fanwort distribution

Variable milfoil distribution

Purple bladderwort distribution

Fine bladderwort distribution

Coarse bladderwort distribution

Water celery distribution

Bushy naiad distribution

Filamentous green algae distribution

Robbins’ pondweed distribution

Bigleaf pondweed distribution

White water lily distribution

Yellow water lily distribution

Fanwort over depth

Variable milfoil over depth

Purple bladderwort over depth

Water celery over depth

Robbins pondweed over depth

Fanwort over substrate

Variable milfoil over substrate

Purple bladderwort over substrate

Water celery over substrate

Robbins’ pondweed over substrate

Cover around the lake

Biovolume around the lake

Cover vs. depth

Biovolume vs. depth

Fanwort vs. depth

Variable milfoil vs. depth

Robbins’ pondweed vs. depth

Fanwort vs. depth

Cover vs. substrate

Biovolume vs. substrate

Fanwort vs. substrate

Variable milfoil vs. substrate

Robbins’ pondweed vs. substrate

Water celery vs. substrate

Cover vs. treatment

Fanwort vs. treatment

Variable milfoil vs. treatment

2003 vs survey results Differences between 2003 and 2012 using only 2003 sites Differences between all 2012 data and reduced data set

Future survey considerations Reduction from 584 points to 292, then to 193, then to146 does not change overall conclusions Cutting shallow water sites in half does not alter conclusions As long as survey points are not selected with bias, smaller effort surveys can provide accurate appraisal of conditions

Treatment considerations Variable milfoil is decreasing in occurrence (53% in 2003 to about 30% in 2012) Fanwort is increasing in occurrence (10% in 2003 to 45% in 2012) Bigleaf pondweed and nitella abundance down Eurasian milfoil and waterweed seemingly eradicated

Treatment considerations Treatment would need to extend to all areas <20 ft deep if fanwort to be controlled, 15 ft for variable milfoil Treatment of coves and shoreline areas is a maintenance activity if other infested areas go unaddressed Drawdown and dredging not feasible Follow up with hand harvesting or benthic barriers may prolong benefits, but not very efficient for larger areas

Treatment considerations Biocontrols unavailable Alternative herbicides can be considered as they become available and experience is gained Current approach appears best in light of plant community features, budgetary constraints, and regulatory limitations

The End QUESTIONS? I’ll drink to that!