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Science in relation to risk

 

DISCUSSION SESSION

Facilitator: Dr Alan Inman, Defra Plant Health Division
Short talks by: Dr Claire Sansford, Central Science Laboratory Dr Joan Webber, Forest Research
Rapporteur: Dr Martin McPherson, Stockbridge Technology Centre Ltd

Following short introductory presentations from Dr Sansford on the Principles of Plant Health Risk Analysis’ and Dr Webber on ‘Science in relation to P. ramorum & P. kernoviae’ to fill some of the knowledge gaps (both presentations are available – see left hand menu), Dr. Alan Inman led a discussion session to explore what the key questions & issues relating to these pathogens were and to identify areas where additional research may be needed.

It was highlighted that Key Research Findings (pdf) were summarised in a document available on the Defra Plant Health website. Final research project reports were also available on the Defra website at: http://www.defra.gov.uk/planth/pramorum6.htm. The EU RAPRA project website was also a good source of information, especially the host database: http://rapra.csl.gov.uk/

Discussion was fairly wide ranging and can be outlined in four broad areas:-

1. Epidemiology
It was evident from discussion that there remain many unanswered questions, though some may be covered with existing R&D programmes. Areas of specific interest included:-

a. Soil persistence – it’s not clear how long the pathogens survive in the soil in proximity to and in the absent of host roots, though there was data from Defra-funded research projects for survival in soil/debris.
b. Systemic infection – does this occur and what is the potential significance?
c. Dispersal in water – data available for P. ramorum though less known about P. kernoviae in this respect.
d. Root infection – can the anecdotal information from the US be substantiated; the EU RAPRA project has some work in progress.
e. Dispersal by animals, birds or invertebrates. What is the risk, if any. Data was available from the USA and some observations from the UK.
f. Risk assessment for wood products e.g. bark mulch, green-waste compost etc.
g. Disposal of infected material needs reconsideration with respect to the option of burial…at least until more information is available on both soil survival and dispersal in water. There was concern that deep burial on site might result in contamination of water courses.
h. The issue of inoculum potential was raised though it was pointed out that a considerable amount of R&D had already been undertaken in this regard and it was not clear that more was needed. To review perhaps?
i. Wind dispersal…is this possible long distance via dust, leaf litter etc? Scientists flagged up research in the USA (California and Oregon) and in the UK.

2. Environmental Influences
A claim was made that we need more information relating to potential for various environmental impacts on host susceptibility e.g. soil acidity impacting on both pathogen and host. No scientific support currently available for such hypotheses, though equally no strong evidence to refute either. In the USA, there was some evidence that ‘healthier’ trees were often more at risk, i.e those with higher stem water potentials. Scientists were urged to keep an open mind to possibilities and all parties to gather evidence where available. This issue was perhaps the most controversial of all discussions in the session.

Also, comment about potential impact on use of glyphosate around nursery sites and effect on host susceptibility and symptom expression in pathogen.

3. Host Taxonomy
Brief discussion regarding relative susceptibility of hosts and cultivars in susceptible species. A specific area of concern was the taxonomy of Rhododendron spp. (“It’s a mess” someone quoted) and additional research requested in this area. It was suggested that data from existing surveys might be useful in highlighting very susceptible cultivars of certain species.

4. Pathogen Taxonomy
The two different A1 & A2 mating types and the risk of recombinants were seen as a potential threat to the industry and environment. It was noted that the EU populations of P. ramorum appeared to be more uniform and pathogenic than those from the USA though it was also noted that they don’t reproduce readily, presumably under artificial conditions in the laboratory, and therefore the risk of novel variants is lower than in P. infestans. The general consensus of this brief discussion was that it warranted ongoing concern. Regular monitoring of the populations dynamics was deemed appropriate so that the industry can react should any new situation arise.

 

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Page last modified: 6 Nov 2006
Page published: 25 Nov 2005

Department for Environment, Food and Rural Affairs