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Figure 2: Control treatment observations.
Results
•	First 3 years of results are now in publication
•	It is clear that there are no short-term solutions for controlling knotweed
•	Physical methods are ineffective due to significant rhizome energetic reserves and
also encourage spread (Figure 2A)
•	Most herbicides are formulated and tested on annual plant species (e.g. synthetic
auxins), with significant implications for control of deep-rooted, rhizome-forming
species such as knotweed (Figure 2B)
•	Rhizome exhibits strong seasonal changes in herbicide uptake - crucial for optimis-
ing control treatment performance (Figures 2C & D)
Wider application
•	Our approach and results are not only relevant for the control of invasive plants
that are resilient to control treatments, but also problematic agricultural weed spe-
cies with extensive rhizomes such as Field bindweed (Convolvulus arvensis) and deep
root systems such as Docks (Rumex spp.) and Creeping thistle (Cirsium arvense)5,6
•	Further, control based on plant life history traits and physiology also holds promise
for control of annual invasive plants and weeds in agricultural systems
How are we testing control response?
Trialling 24 proven and novel knotweed physiochemical control methods at three
sites in South Wales (Figure 1).
Field trial plots consist of:
•	225 m2
treatment area (15×15 m)
•	6×4 m2
monitoring patches, assigned at random
•	Treatment plots are replicated in triplicate and treated in their entirety
•	Control plots received no treatment
Monitoring patch data capture:
•	Aboveground knotweed growth parameters (e.g. stem diameter)
•	Plant stress measures (e.g. photosystem II efficiency)
•	Vascular plant species diversity
•	Soil parameters
This represents the largest knotweed control experiment ever undertaken and in-
cludes the greatest number of treatments ever trialled for the control of a single in-
vasive species (the previous best is 6!). Further, it is one of the longest running inva-
sive species field trials, worldwide4
.
Overview
Japanese knotweed (Fallopia japonica var. japonica) has well documented ecological
and socioeconomic impacts that are costly to remedy.
Ecological impacts:
•	Reduced habitat availability and quality
•	Disruption of terrestrial and freshwater food webs1
Socioeconomic impacts:
•	Built environment (e.g. development sites)
•	Recreation and landscape (e.g. angling)
•	Maintenance control costs for knotweed in the UK are £165.6 million per annum
and eradication would cost in excess of £1.5 billion2,3
Field trial rationale
Knotweed is an internationally recognised problem. However, previous control re-
search has been small-scale, piecemeal and crucially, of short duration. Due to limited
understanding of plant-herbicide interactions and long-term control outcomes, prac-
titioners and stakeholders were not able to make good, evidence-based decisions on
how to control these species effectively, efficiently and sustainably.
Our ability to control knotweed relies on how well we understand the plant, herbi-
cides and physical treatments that we use to control it. Additionally, with no long-
term studies of knotweed control, it was not possible to adequately predict control
response in the long-term.
Aims
Based on our new understanding of knotweed biology, we established a large-scale
and long-term field experiment to:
•	Test control efficacy of widely applied and novel control methods
•	Assess control method costs and environmental impacts
•	Investigate site restoration following knotweed control
References:
[1] Gerber et al. 2008; [2] Shaw et al. 2009; [3] Williams et al. 2010; [4] Kettenring & Adams 2011; [5] Hujerová et al
2013; [6] Tautges et al. 2016.
Covering treatment
888 DAT
Tordon 22K®
& Glyfos ProActive®
797 DAT
11.20 L ha-1
(2.69 kg AE ha-1
) picloram &
10.00 L ha-1
(3.60 kg AE ha-1
) glyphosate
Single spray treatment
Glyfos ProActive®
404 DAT
10.00 L ha-1
(3.60 kg AE ha-1
) glyphosate
Cut & fill treatment
Glyfos ProActive®
407 DAT
244.44 L ha-1
(80.00 kg AE ha-1
) glyphosate
Acknowledgements:
•	 Dr Tim Rich and Dr John Bailey for advice and support
•	 Mr Gethin Bowes, Dr Jonathan Newman, Dr Andrew
Skibo, Mr Art Gover, Dr Charles Hipkin, Dr Lois Child,
Dr David Stock and Mr Barrie Hunt for their extensive
practical and technical advice and for equipment provi-
sion
•	 Prof Bruce Osborne for discussions and guidance
•	 Mr Sean Hathway for supplying sites
•	 Mr Dan Montagnani for supplying detailed site reports
Figure 1: Aerial views of field trial sites in South Wales.Where A = Lower Swansea
Valley Woods; B = SwanseaVale Nature Reserve and C = Taffs Well (nr. Cardiff)
Part-funded by the European Social Fund (ESF) through the Welsh
Government with Swansea University and Complete Weed Control Ltd.
Disentangling Japanese Knotweed
Daniel Jones1,2
, Gareth Bruce1,2
, Mike Fowler1
, Rhyan Law-Cooper1,2
, Ian Graham3
, Alan Abel3
,
F. Alayne Street-Perrott4
& Daniel Eastwood1
1
Department of Biosciences, Swansea University, UK; 2
Advanced Invasives Ltd., Institute of Life Science, Swansea University, UK;
3
Complete Weed Control Ltd., Newton Aycliffe, UK; 4
Department of Geography, Swansea University, UK
Dr Dan Jones contact information:
Email - daniel@advancedinvasives.com | Mobile - +44 (0)7967 408844
A B C D
BA
C

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Disentangling Japanese Knotweed

  • 1. Figure 2: Control treatment observations. Results • First 3 years of results are now in publication • It is clear that there are no short-term solutions for controlling knotweed • Physical methods are ineffective due to significant rhizome energetic reserves and also encourage spread (Figure 2A) • Most herbicides are formulated and tested on annual plant species (e.g. synthetic auxins), with significant implications for control of deep-rooted, rhizome-forming species such as knotweed (Figure 2B) • Rhizome exhibits strong seasonal changes in herbicide uptake - crucial for optimis- ing control treatment performance (Figures 2C & D) Wider application • Our approach and results are not only relevant for the control of invasive plants that are resilient to control treatments, but also problematic agricultural weed spe- cies with extensive rhizomes such as Field bindweed (Convolvulus arvensis) and deep root systems such as Docks (Rumex spp.) and Creeping thistle (Cirsium arvense)5,6 • Further, control based on plant life history traits and physiology also holds promise for control of annual invasive plants and weeds in agricultural systems How are we testing control response? Trialling 24 proven and novel knotweed physiochemical control methods at three sites in South Wales (Figure 1). Field trial plots consist of: • 225 m2 treatment area (15×15 m) • 6×4 m2 monitoring patches, assigned at random • Treatment plots are replicated in triplicate and treated in their entirety • Control plots received no treatment Monitoring patch data capture: • Aboveground knotweed growth parameters (e.g. stem diameter) • Plant stress measures (e.g. photosystem II efficiency) • Vascular plant species diversity • Soil parameters This represents the largest knotweed control experiment ever undertaken and in- cludes the greatest number of treatments ever trialled for the control of a single in- vasive species (the previous best is 6!). Further, it is one of the longest running inva- sive species field trials, worldwide4 . Overview Japanese knotweed (Fallopia japonica var. japonica) has well documented ecological and socioeconomic impacts that are costly to remedy. Ecological impacts: • Reduced habitat availability and quality • Disruption of terrestrial and freshwater food webs1 Socioeconomic impacts: • Built environment (e.g. development sites) • Recreation and landscape (e.g. angling) • Maintenance control costs for knotweed in the UK are £165.6 million per annum and eradication would cost in excess of £1.5 billion2,3 Field trial rationale Knotweed is an internationally recognised problem. However, previous control re- search has been small-scale, piecemeal and crucially, of short duration. Due to limited understanding of plant-herbicide interactions and long-term control outcomes, prac- titioners and stakeholders were not able to make good, evidence-based decisions on how to control these species effectively, efficiently and sustainably. Our ability to control knotweed relies on how well we understand the plant, herbi- cides and physical treatments that we use to control it. Additionally, with no long- term studies of knotweed control, it was not possible to adequately predict control response in the long-term. Aims Based on our new understanding of knotweed biology, we established a large-scale and long-term field experiment to: • Test control efficacy of widely applied and novel control methods • Assess control method costs and environmental impacts • Investigate site restoration following knotweed control References: [1] Gerber et al. 2008; [2] Shaw et al. 2009; [3] Williams et al. 2010; [4] Kettenring & Adams 2011; [5] Hujerová et al 2013; [6] Tautges et al. 2016. Covering treatment 888 DAT Tordon 22K® & Glyfos ProActive® 797 DAT 11.20 L ha-1 (2.69 kg AE ha-1 ) picloram & 10.00 L ha-1 (3.60 kg AE ha-1 ) glyphosate Single spray treatment Glyfos ProActive® 404 DAT 10.00 L ha-1 (3.60 kg AE ha-1 ) glyphosate Cut & fill treatment Glyfos ProActive® 407 DAT 244.44 L ha-1 (80.00 kg AE ha-1 ) glyphosate Acknowledgements: • Dr Tim Rich and Dr John Bailey for advice and support • Mr Gethin Bowes, Dr Jonathan Newman, Dr Andrew Skibo, Mr Art Gover, Dr Charles Hipkin, Dr Lois Child, Dr David Stock and Mr Barrie Hunt for their extensive practical and technical advice and for equipment provi- sion • Prof Bruce Osborne for discussions and guidance • Mr Sean Hathway for supplying sites • Mr Dan Montagnani for supplying detailed site reports Figure 1: Aerial views of field trial sites in South Wales.Where A = Lower Swansea Valley Woods; B = SwanseaVale Nature Reserve and C = Taffs Well (nr. Cardiff) Part-funded by the European Social Fund (ESF) through the Welsh Government with Swansea University and Complete Weed Control Ltd. Disentangling Japanese Knotweed Daniel Jones1,2 , Gareth Bruce1,2 , Mike Fowler1 , Rhyan Law-Cooper1,2 , Ian Graham3 , Alan Abel3 , F. Alayne Street-Perrott4 & Daniel Eastwood1 1 Department of Biosciences, Swansea University, UK; 2 Advanced Invasives Ltd., Institute of Life Science, Swansea University, UK; 3 Complete Weed Control Ltd., Newton Aycliffe, UK; 4 Department of Geography, Swansea University, UK Dr Dan Jones contact information: Email - daniel@advancedinvasives.com | Mobile - +44 (0)7967 408844 A B C D BA C