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Scotland’s Crayfish Crisis Zara Gladman [email protected]
Transcript

Scotland’s Crayfish Crisis

Zara [email protected]

Overview

Scotland’s crayfish crisis: some background

Tackling the crisis

Biodiversity and environmental change

Scotland’s crayfish crisis: some background

American signal crayfish(Pacifastacus leniusculus)

Scotland’s crayfish crisis: some background

American signal crayfish(Pacifastacus leniusculus)

Large, freshwater, decapod crustacean

Native to western North America

Imported to Britain in 1970s for aquaculture

First recorded in Scotland in Galloway, 1995

Scotland’s crayfish crisis: some background

Non-native invasive species cited as one of the top 5 drivers of ecosystem change

Serious threat to biodiversity listed under ‘Species Action Framework’ in 2007

Scotland’s crayfish crisis: some background

Where is it?

How can we get rid of it?

What is it doing?

Tackling the crisis

Where is it? 1. Distribution

How can we get rid of it? 2. Control

What is it doing? 3. Impact

Tackling the crisis

3 broad aims of PhD

Where is it? 1. Distribution

How can we get rid of it? 2. Control

What is it doing? 3. Impact

Tackling the crisis

3 broad aims of PhD

1. Distribution

Fine-scale distribution of signal crayfish largely unknown

For effective control/containment, we must know where it is!

First aim: develop a protocol for detecting crayfish

applied across Scotland

1. Distribution

Compared the crayfish detection ability of four active sampling techniques

30 riffles on upper River Clyde

1. Hand searching 2. Electrofishing 

(1, 2, 3 runs)3. Kick sampling 4. Surber sampling

1. Distribution

Results: combination of kick sampling and 3 runs of electrofishing best chance of detecting signal crayfish (Gladman et al., accepted)

Location River Catchment Fishery Trust Undertaking the Survey

Upper Clyde Clyde Clyde River Foundation

River North Esk (ponds); Lugar Burn/main stem North Esk Esks DSFBs

Pow Burn South Esk Esks DSFBs

Rankeillour Burn (Fife) Eden Forth Fisheries Trust

River Teith (pond and ditches) Forth Forth Fisheries Trust

River Tyne (stillwater fishery, East Lothian) East Lothian Tyne Forth Fisheries Trust

Tiel Burn (Fife) Tiel Forth Fisheries Trust

Murray Burn Water of Leith Forth Fisheries Trust

Kirkcudbrightshire Dee Galloway Fisheries Trust

Skyre Burn Fleet Galloway Fisheries Trust

River Nairn Nairn Ness and Beauly Fisheries Trust

Dighty Water (Dundee) Dighty Tay DSFB

River Earn Earn Tay DSFB

River Ardle (pond and small stream) Ericht Tay DSFB

Shee Water (pond and small stream) Ericht Tay DSFB

Rivers Ettrick and Till Tweed Tweed Foundation

Kirkbank (Teviot Water) Tweed Tweed Foundation

• Protocol

1. Distribution

Sinclair, CA (2009). Fine scale mapping of signal crayfish distribution in Scotland, Scottish Natural Heritage Commissioned Report, Project 26686.

1. Distribution

. . . So where is it?

2. Control

Physical

Chemical

Biological

Case study: Loch Ken’s crayfish crisis

2. ControlCrayfish crisis 'looming' on loch

Loch Ken’s crayfish crisis

Summer 2009: Marine Scotland funded an intensive 4-month trapping programme:

Assess the scale of the infestation

Assess the feasibility of control

Opportunity for research:

Effect of intensive trapping on the population

Two mark-and-recapture projects: one before and one after the trapping programme

2. Control Loch Ken’s crayfish crisis

Crayfish sampled at 3 sites (transects of 15 creels, 400 m apart) during two sessions: before (May/June) and after (September) the trapping programme

2. Control Loch Ken’s crayfish crisis

2. Control Loch Ken’s crayfish crisis

Total catch

3879 crayfish before trapping programme

3205 crayfish after trapping programme

. . . very little effect?!

2. Control Loch Ken’s crayfish crisis

Numbers of males and females caught during the two mark and recapture sessions before (May/June) the 

removal programme and after (September) the removal programme 

Denotes within‐sex pairwise

comparison with statistically significant difference p<0.01

2. Control

Site 1 Site 2 Site 3

Before After Before After Before After

1 M :0.42 F

1 M :1.04 F

1 M :0.37 F

1 M : 1.54 F

1 M :0.40 F

1 M :0.85 F

. . . Sex is important!

Loch Ken’s crayfish crisis

2. Control

. . . Sex is important!

Due to:

Bias of trapping towards large males

Changes in reproductive state of females: berried females in May are trap shy; egg release in summer

Numbers of males and females caught during the two mark and recapture sessions before (May/June) the 

removal programme and after (September) the removal programme 

Denotes within‐sex pairwise

comparison with statistically significant difference p<0.01

Loch Ken’s crayfish crisis

2. Control

Density estimates

Population estimates from mark and recapture data were used to make estimates of density (based on a trapping radius of 100 m2, Accosta & Perry, 2000)

Range 1.06 – 9.05 crayfish per m-2

Very high densities compared with other lakes:

Lake Billy Chinook: 0.24 c.p.m-2 and 1.13 c.p.m-2

Lake Donner: 0-1.15 c.p.m-2

Lake Tahoe: 0.53-8.38 c.p.m-2

Loch Ken’s crayfish crisis

2. Control

Other observations

Mean size of crayfish reduced

Significant for males

Movements

At least 800m in two weeks; 3 km in 6 months

Loch Ken’s crayfish crisis

2. Control

Summary

Trapping significantly reduced males; effect on females complicated by trap bias/reproductive status sex ratio skewed towards females

Mean size of crayfish reduced

Crayfish capable of significant movements

High densities mean loss to biodiversity likely to be significant

Loch Ken’s crayfish crisis

Biodiversity and environmental change

Alien species are a major threat to biodiversity

Very difficult (impossible?) to reverse changes

Prevention is preferable!

Research is important in helping us understand ecological problems . . . and deal with them!

Thanks to . . .

Colin Adams Colin Bean Jo Long Willie Yeomans

[email protected]


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