Case study:Giving up the Weed

From RESTORE
Jump to: navigation, search
0.00
(0 votes)


To discuss or comment on this case study, please use the discussion page.


Location: 52° 2' 43", -3° 12' 4"
Edit location
Loading map...
Left click to look around in the map, and use the wheel of your mouse to zoom in and out.


Project overview

Edit project overview
Status In progress
Project web site http://www.wyeuskfoundation.org/projects/weed.php
Themes Habitat and biodiversity, Monitoring
Country England
Main contact forename Stephen
Main contact surname Marsh-Smith
Main contact user ID
Contact organisation Wye & Usk Foundation
Contact organisation web site http://www.wyeuskfoundation.org/
Partner organisations Environment Agency Wales, Countryside Council for Wales, Natural England, Keep Wales Tidy
Parent multi-site project
This is a parent project
encompassing the following
projects
No
Project picture

Project summary

Edit project overview to modify the project summary.


In November 2007, the Esmee Fairbairn Foundation granted funds to the Wye & Usk Foundation for an invasive weeds eradication project in the Wye and Usk catchments. The three year project was supported by the Environment Agency Wales, Countryside Council for Wales, Natural England and Keep Wales Tidy. Our catchments are under a very considerable threat from at least three species of invading weed. Rivers and streams are the ideal vector for carrying seeds and plants downstream. They can, however invade upstream via a number of vectors. Our concern is for the loss of biodiversity and, since these plants smother the native species that armour the river banks, the increased erosion that will occur.


The invading trio of species includes:


Giant Hogweed - Heracleum mantegazzianum

• Perennial – grows 5 -7m.

• Member of parsley family.

• Arrived in UK 1893 from Caucasus.

• Sap causes serious rashes when skin exposed to sunlight. Can cause blindness.

• Can be controlled by spraying, grazing, cutting or digging- up.

• Spraying with Glyphosphate (Round Up) is a successful treatment.

• Spread by rivers and seeds last 3 or more years.


Japanese Knotweed - Fallopia japonica

• Arrived in UK (South Wales) late 19th century.

• 2 – 3m height but spreads 7m horizontally.

• Perennial Rhizome.

• Edible (the early shoots!).

• Female only in UK but can Hybridise with Himalayan Knotweed.

• Can be spread via small cut pieces.

• Estimated to cost £1.56 billion to eradicate in UK (2007).

• Significant issue for developers (eg Olympic grounds).

• Can be sprayed with round up but can prove resistant.

• Can hybridise with Himalayan Knotweed which has male flowers.


Himalayan balsam - Impatiens glandulifera

• Arrived UK in 1839.

• Annual - grows 2m typically on river banks.

• Suffocates native plants if unchecked.

• Approx 800 seeds can last 2 years.

• Can be treated by spraying, pulling or cutting.

• Causes increased erosion to river banks.


Giving up the Weed: How the project operated.

The grant was used to pay for:

• Plotting of all Invasive weeds on a database as currently known and received from reports (years 1-3).

• Training five staff in the techniques of spraying (year 1).

• Eradicating Giant Hogweed in the Wye (Glasbury downstream for over 80km in the spring (Years 1-3).

• Eradicating all Himalayan Knotweed in both catchments (year 1).

• Eradicating all Japanese Knotweed starting from extremities of the Usk and Wye (years 1-3).

• Developing volunteer networks to manage Himalayan balsam.

• Investigating the legal position in respect of liability for spread.

• Study the effects of fencing out buffer strips and the effect on invasive weeds.


Budget:

The Esmee Fairbairn Foundation grant of £94,000 over three years was added to contributions from WUF, Environment Agency Wales, Countryside Council for Wales and Natural England to give a total budget of just under £150,000.


Project Results:

The project enabled the development of a logistical system to manage the massive problem of Giant Hogweed and Japanese Knotweed in the Usk and Wye. In the first three years, over 125km of double bank was sprayed for Giant Hogweed (4,000+ plants), with 337 stands of Japanese knotweed, 3 stands of Himalayan knotweed and 1 stand of Lesser knotweed also sprayed.

The project also extended to mink and Signal crayfish trapping in areas of Wales where water voles may still be present and WUF also publicised the spread of other invasives such as the Killer Shrimp (Dikerogammerus villosus), which have been found in Cardiff Bay and a lake near Port Talbot.


2011 Onwards...

Since 2011, the invasive species eradication programme has continued with funding from Natural Resources Wales, Natural England, Beacons Trust and riparian owners. Enemy number one - Giant hogweed - has almost been seen off although seeds can remain in the soil for more than eight years. Vigilance is therefore required to ensure any emerging seeds are dealt with before developing into seeding adult plants.

Japanese knotweed is reducing following our regular autumn spraying and we have found that spraying when the plant is in flower gives a much greater chance of eliminating it. Checking for regrowth is an important part of it – we rely on anglers, walkers and owners to keep us informed of any new stands.

Thus far we have treated 3,336 stands of Giant hogweed covering over 455km river, 488 stands of Japanese knotweed, 4 of Himalayan knotweed and 4 of Lesser knotweed.


Himalayan Balsam

Once it seemed that Himalayan balsam (HB) would continue its spread unhindered. Not only was it extremely successful in spreading downstream (and even upstream) but it is spreading inland from rivers too. However, the warm, dry spring of 2012 caused seeds to sprout early and young plants were first hit with a sharp April frost, killing any early germination. Then successive floods throughout the year put paid to later plants within the flood zone. Plants further away from the river did well but not everywhere: the Monnow Rivers Association, assisted with funding from this project, have sprayed all HB plants in their catchment and all they have to do now is mop up any missed stragglers.

Eradication can therefore be achieved with determination but for owners of the many hundreds of miles downstream of an infestation, managing the HB on their bank needs to be considered differently: spraying a section can lead to seeds finding it even easier to germinate on bare soil.

Following trials over several years, these are our recommendations for managing HB in these circumstances:

• Cut or pull plants in June/July and leave them where they fall.

• Follow up in early September - there’s always one or two plants that survive or recover.

• Using a hedge trimmer makes this less of a chore. It also deals with brambles, grasses, nettles and small trees.

• Following cutting, native plants recolonise unsprayed areas much more quickly.

• The majority of next year’s infestation comes from the seed of plants growing in the immediate vicinity.


When balsam plants die back in autumn, none of the native bank armouring plants are there to resist winter floods. Controlling total balsam cover will therefore help to reduce erosion. When all the Hogweed and Knotweed is under control, we will be focusing our efforts solely against balsam.

Monitoring surveys and results

This case study hasn’t got any Monitoring survey and results, you can add some by editing the project overview.

Lessons learnt

This case study hasn’t got any lessons learnt, you can add some by editing the project overview.


Image gallery


ShowHideAdditionalImage.png


Catchment and subcatchment



Site

Name
WFD water body codes
WFD (national) typology
WFD water body name
Pre-project morphology
Reference morphology
Desired post project morphology
Heavily modified water body
National/international site designation
Local/regional site designations
Protected species present
Invasive species present
Species of interest
Dominant hydrology
Dominant substrate
River corridor land use
Average bankfull channel width category
Average bankfull channel width (m)
Average bankfull channel depth category
Average bankfull channel depth (m)
Mean discharge category
Mean annual discharge (m3/s)
Average channel gradient category
Average channel gradient
Average unit stream power (W/m2)


Project background

Reach length directly affected (m)
Project started 2007/10/01
Works started
Works completed
Project completed
Total cost category
Total cost (k€)
Benefit to cost ratio
Funding sources

Cost for project phases

Phase cost category cost exact (k€) Lead organisation Contact forename Contact surname
Investigation and design
Stakeholder engagement and communication
Works and works supervision
Post-project management and maintenance
Monitoring



Reasons for river restoration

Mitigation of a pressure Invasive species
Hydromorphology
Biology
Physico-chemical
Other reasons for the project


Measures

Structural measures
Bank/bed modifications
Floodplain / River corridor
Planform / Channel pattern
Other
Non-structural measures
Management interventions Removal of invasive species
Social measures (incl. engagement) Community Education
Other


Monitoring

Hydromorphological quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Biological quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Physico-chemical quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Any other monitoring, e.g. social, economic

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative


Monitoring documents



Additional documents and videos


Additional links and references

Link Description

Supplementary Information

Edit Supplementary Information