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New Zealand mud snails
(Potamopyrus antipodarum)
In Capitol Lake
• Small aquatic snail
• Parthenogenic
• High reproductive
potential
▫ 20-120 offspring/year
• High-density populations
▫ 100,000-500,000/m2
• Tolerant of moderate
salinity levels (17-24 pss)
Impacts
• Outcompete native gastropods by consuming large
quantities of primary production
• Do not serve as an equivalent food source – NZMS
pass through fish guts undigested.
• Restricted recreational opportunities.
• Increased costs to aquaculture and municipal water
control facilities.
Western Expansion
Vectors
• Fish hatcheries and associated stocking operations
• Recreational watercraft and trailers
• Anglers and hunters
• Sand and gravel mining, dredging
• Commercial shipping
• Pets, fish and wildlife
• Natural resource management activities
Response
▫ Fish and Wildlife –
state and federal
▫ General
Administration
▫ Ecology
▫ Natural Resources
▫ City of Olympia
▫ Invasive Species
Council
• October 2009 – snails found
• November 2009
▫ Agencies notified
▫ Response work group formed
▫ Closed lake
• December 2009
▫ Partial lake drawdown + Freeze
• March 2010
▫ Lake drained and filled with
water from Budd Inlet
• July 2010
▫ Survey around lake
Freeze results
0 1 2 3 4 5
Time (days)
0.0
0.2
0.4
0.6
0.8
1.0
Survivalrate
Day 0 ~ 20,000 NZMS/m2
Day 5 ~ 400 NZMS/m2
Saltwater back flush
• 25 sites sampled
• Day 1: Fill water 28.7 pss
• Salinity levels declined
with freshwater inputs
from Deschutes River
• NZMS likely exposed to
salinities above 20 for 7-
8 hours.
12% mortality from backflush
Impact on NZMS
Impact on resident benthic invertebrates
• Negative impact
▫ Abundance
▫ Species richness
• Community could
recover to similar
diversity and
abundance
▫ Overall community
structure (based on
feeding groups)
remained similar before
and after backflush.
0
1000
2000
3000
4000
5000
6000
7000
8000
9000
Pre-Backflush Treatment Post-Backflush Treatment
AverageTotalAbundanceofBenthicMacroinvertebrate
Organisms/M2
Pre-Backflush Post-Backflush
AverageTotalAbundance/M2
What’s next?
• Continue containment
• Freeze
• Permanent plots established to look at long-term
response
• Small-scale trials of higher salt concentrations or
other treatments
www.invasivespecies.wa.gov
wendy.brown@invasivespecies.wa.gov

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Invasive New Zealand mud snails threaten Capitol Lake

  • 1. New Zealand mud snails (Potamopyrus antipodarum) In Capitol Lake
  • 2.
  • 3.
  • 4. • Small aquatic snail • Parthenogenic • High reproductive potential ▫ 20-120 offspring/year • High-density populations ▫ 100,000-500,000/m2 • Tolerant of moderate salinity levels (17-24 pss)
  • 5. Impacts • Outcompete native gastropods by consuming large quantities of primary production • Do not serve as an equivalent food source – NZMS pass through fish guts undigested. • Restricted recreational opportunities. • Increased costs to aquaculture and municipal water control facilities.
  • 7.
  • 8. Vectors • Fish hatcheries and associated stocking operations • Recreational watercraft and trailers • Anglers and hunters • Sand and gravel mining, dredging • Commercial shipping • Pets, fish and wildlife • Natural resource management activities
  • 9. Response ▫ Fish and Wildlife – state and federal ▫ General Administration ▫ Ecology ▫ Natural Resources ▫ City of Olympia ▫ Invasive Species Council • October 2009 – snails found • November 2009 ▫ Agencies notified ▫ Response work group formed ▫ Closed lake • December 2009 ▫ Partial lake drawdown + Freeze • March 2010 ▫ Lake drained and filled with water from Budd Inlet • July 2010 ▫ Survey around lake
  • 10.
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  • 12. Freeze results 0 1 2 3 4 5 Time (days) 0.0 0.2 0.4 0.6 0.8 1.0 Survivalrate Day 0 ~ 20,000 NZMS/m2 Day 5 ~ 400 NZMS/m2
  • 14.
  • 15.
  • 16. • 25 sites sampled • Day 1: Fill water 28.7 pss • Salinity levels declined with freshwater inputs from Deschutes River • NZMS likely exposed to salinities above 20 for 7- 8 hours.
  • 17. 12% mortality from backflush Impact on NZMS
  • 18. Impact on resident benthic invertebrates • Negative impact ▫ Abundance ▫ Species richness • Community could recover to similar diversity and abundance ▫ Overall community structure (based on feeding groups) remained similar before and after backflush. 0 1000 2000 3000 4000 5000 6000 7000 8000 9000 Pre-Backflush Treatment Post-Backflush Treatment AverageTotalAbundanceofBenthicMacroinvertebrate Organisms/M2 Pre-Backflush Post-Backflush AverageTotalAbundance/M2
  • 19. What’s next? • Continue containment • Freeze • Permanent plots established to look at long-term response • Small-scale trials of higher salt concentrations or other treatments