Extension Note BC Journal of Ecosystems and Management British Columbia’s Northern Interior Forests Stand Establishment Decision Aid

Larry McCulloch1 and Alex Woods2 Introduction

Dothistroma needle blight, also known as red band needle blight, is caused by the Dothistroma septosporum. It affects over 60 of in 45 countries and is considered the most destructive pine needle disease in the world. All pine species native to British Columbia are susceptible and the fungus is widely distributed wherever host species can be found. Infection is caused by rain splash and air dispersal of the spores. In the , it has been a major problem for decades. In British Columbia, however, damage levels from this pathogen have historically been low. Recent widespread defoliation, mortality (including mature tree mortality), and plantation failure caused by Dothistroma in the northwest portion of the province may be a result of changing climatic conditions that allow the fungus to develop in a way that was not previously possible. The Stand Establishment Decision Aid (seda) format has been used to extend information on a variety of vegetation and forest health concerns in British Columbia. The two-page seda presented in this extension note was developed to summarize information that provincial forest managers will need to mitigate the impacts of Dothistroma needle blight. The first page provides information on susceptible stand types, disease biology, hazard ratings, and appropriate management practices. The second page outlines forest productivity considerations and risks to human health. A resource and reference list that readers can use to find more detailed information is also included. Most reference material that is not available online can be ordered through libraries or the Queen’s Printer at: www.qp.gov.bc.ca Acknowledgements The preparation and publication of this decision aid was supported by the British Columbia Ministry of Forests and Range through the Forest Investment Account–Forest Science Program. keywords: climate change, Dothistroma needle blight, Dothistroma septosporum, forest health, red band needle disease, tree species deployment.

Contact Information 1 Principal, LM Forest Resource Solutions Ltd. PO Box 880, Smithers, BC V0J 2N0. Email: [email protected] 2 Forest Pathologist, BC Ministry of Forests and Range, Northern Interior Region, Regional Service Centre, Bag 6000, 3333 Tatlow Road, Smithers, BC V0J 2N0. Email: [email protected]

article received: June 26, 2007 article accepted: October 3, 2008

JEM — Vo l u me 10, Nu m b e r 1 Published by Forrex Forum for Research and Extension in Natural Resources McCulloch, L. and A. Woods. 2009. BritishJ EMColumbia’s — Vo l u northernme 10, Ninterioru m b e r forests: 1 Dothistroma Stand Establishment 1 Decision Aid. BC Journal of Ecosystems and Management 10(1):1–3. www.forrex.org/publications/jem/ISS50/vol10_ no1_art1.pdf mcculloch and w o o d s

in

will

in 2025,

which

Such minimize not that

in

subzones sites year

to

changes imperative.

help promise.

replacement

lodgepole

is the bec a 2006).

of should

may as By ) zone, more effort

program

mix ponding

shown conditions predicted is zone

pine Wang

sbs

conditions air

anticipated sbs areas.

have

and

research species

cold breeding

climatic both create provenances

a Douglas-fir

pine

in tree to

future.

a and regenerated

genetic

Hamann the

of shift

potential high-hazard

given

a with

in

Austrian in in (see

identify further establishing establishing

and

20% zone

) proportion

experience

ich spread. and infection a species of establishment require areas high-hazard in high-hazard be favoured not should mix; pine areas. clearcutting areas. high-hazard The exceed to the the northern portion of Cedar–Hemlock the Interior resemble closely more ( disease root hazard. and climate for a high willa shift hazard these make areas Dothistroma the warmer of even in some pine for acceptable an as listed currently not is it where in which Douglas-fir might species. Subzones with be carefully chosen must be acceptable consideration Dothistroma-resistant other In developed. and identified are pine trials ponderosa, with host-resistance locations, radiata, genetic some shows itself fungus Dothistroma The diversity; managers will be needed to prevent and control this disease if this disease and control will prevent be needed to be a to lodgepole continues pine for management described are below options treatment Some priority. of stage by intervention. management Harvesting and moderate- for • Ensure prescriptions silviculture Management considerations Management pine species caused the damage to recently, Until in British Columbia by Dothistroma needle blight and the changing climate With was of little concern. drier areas into spread to Dothistroma for potential ( Spruce as the Sub-Boreal such avoid pine, • If re-establish to is the intention Stand establishment • Regeneration • Consider • Consider years. extended 1–2 take during can 20°C this and 15 factors, ) zone, other . between bec and ich 1 conditions Temperatures will these affect rankings change Climate conditions. climatic current listed, not is unit a biogeoclimatic 2006). If Wang and (see Hamann hazard. be to a significant considered not is Dothistroma Biogeoclimatic of explanation an ( Classification Ecosystem abbreviations. variant and subzone, infection. for optimal are periods moisture of host on land spores If cloud). or mist (e.g., air saturated these can periods high during humidity, of material needles. the unaffected penetrate and germinate causes that a toxin produces the needle.within growth This in diseased bodies needles. Fruiting pigmentation the red small, as dead appear needles on and (pseudothecia) form (see the epidermis right through break that structures dark above). photo side of Depending on cycle. the life complete to new spores release climatic season the growing occur can throughout infections and is moisture 5°C and above are temperatures provided present. rain warm the frequency of and between levels infection 3 or 18°C for exceeding high temperatures daily (i.e., events north-central In August). or in July days consecutive more increasing. is events such the frequency of Columbia, British the to adjacent areas In biology and based known on expert opinion represent Ratings (1991) for Pojar and See Meidinger

b a 1 Hazard ratings • Spores in moisture- distances long be can transported • The growth a period goes through vegetative fungus of fruiting bodies • During mature periods high humidity, of infected needles • Spores previously from released are exists correlation • Recent a strong that indicates research Dave Weaver Dave

fire a been

though also as

has

appear it Mortality

making old).

years

foliage 30

red to

(up

highly are pine) bishop and pine Monterey (e.g., susceptible. affected. severely most often is crown lower extensive susceptible. in this area. lodgepole pine observed in mature affected. worst the areas typically are watercourses pine lodgepole of plantations in managed Columbia British been the stand. has through above), (see the photo the left side of brown reddish green. remains the the base needlesalthough of often the affected were when needles that the spring that Needles clearly. most up show year previous positive best for been are killed earlier have 1–2 years straw-coloured on bands red (dark identification above). needles photo – see side of right in the province • Non-native species established pine • The occurred in northwest have infections severe most Description and biology The • Crowns in appearance. be tufted to thin and tend thin with • In are crowns stands, affected severely Characteristics of susceptible stands • All are Columbia British to species native pine Dothistroma-infected lodgepole pine needles with Dothistroma-infected lodgepole pine needles with characteristic red bands • Cold major along areas and sites ponding air • Needles susceptible. are all ages of • Spots turn the needles on and appear bands and • The identify the disease to year in is best time of Dothistroma Needle Blight – Northern Interior Forest Region Interior Forest Blight – Northern Needle Dothistroma

2 JEM — Vo l u me 10, Nu m b e r 1 dothistroma needle blight–northern interior f o r e s t r e g i o n g ditor, ditor, E xtension xtension E esearch and and esearch R Managing Managing

esearch and and esearch R Forum for for Forum Forum for for Forum V2C 3J4, or email [email protected] email V2C 3J4, or Forrex . For consents, contact: consents, For . Forrex Forrex (Accessed February 2009). m (Accessed Niche breadth, climate change, and reforestation. and reforestation. change, climate breadth, Niche

esources Society and the Province of British Columbia Columbia British of Province the and Society esources (Accessed February 2009). (Accessed R ociety and of all contributing copyright owners. This publication publication This owners. copyright contributing all of and ociety S does not warrant their and accuracy or disclaims expressly any reliability, esources esources uite 702, 235 1st Avenue, Kamloops, BC Kamloops, Avenue, 702, 235 1st uite R , S 1488-4674. Articles or contributions in this publication may be reproduced in in reproduced be may publication this in contributions or Articles 1488-4674. A review. Forest Pathology 34:163–185. Pathology Forest A review. Forrex atural atural

N xtension in Natural Natural in xtension nternet without the written consent of of consent written the without nternet issn Forrex The information and opinions expressed in this publication are those of the respective authors authors respective the of those are publication this in expressed opinions and information The and thereto. relation in liability E © 2009 Copyright in this article this is© 2009 Copyright in property the of and training, educational, in recipient the to charge of free use for form print or electronic acknowledged. fully are authorship and source their that provided activities not-for-profit media, or forms other to application translation, adaptation, reproduction, However, or resale, use, commercial for part, in or whole in works, these of use other any or of consent written the requires redistribution, in in the over public the to accessible made be not may herein contributions and articles the and I (Accessed February 2009). m (Accessed Ecological Monographs 69(3):375–407. 69(3):375–407. Ecological Monographs 79:892–897. Forestry Chronicle www.for.gov.bc.ca/ 55(9):761–769. BioScience change? climate to blight related epidemic hfp/fft/scientific-articles/articles/Woods%20et%20al%202005_Dothistroma%20and%20 f Climate%20Change.pd Natural Resources Canada, Canadian Forest Service, Victoria BC. www.pfc.cfs.nrcan.gc.ca/ BC. Victoria Service, Forest Canadian Canada, Resources Natural February 2009). diseases/ctd/index_e.html (Accessed toxin: Ecology 87:2773–2786. species distribution in British Columbia. www.for.gov.bc.ca/hfd/pubs/Docs/Srs/SRseries. 6. Series Special Report No. BC. Victoria, ht Phytopathology 57:437–441. Epidemiology and control. www.na.fs.fed.us/spfo/ 143. No. and Disease Insect Leaflet Forest Nebr. Lincoln, Service, pubs/fidls/dothistroma/doth.ht in Pinus contorta: climate to

Woods, A. 2003. Species diversity and forest health in northwest British Columbia. British Columbia. health in northwest and forest Species diversity 2003. A. Woods, needle Dothistroma an unprecedented Is 2005. Hamann. A. and Coates, K.D. A., Woods, Resource and reference list and reference Resource of diseases tree Common British Columbia. 1996. Wallis. and G. Morrison, D. E., Allen, band) needle blight (red Dothistroma of dothistromin and the 2004. R.E. Bradshaw, and tree effects of ecosystem on change climate Potential 2006. Wang. and T. A. Hamann, BC Ministry of of British Ecosystems Columbia. Forests, 1991. Pojar. and J. D. Meidinger, pines: needle and ponderosa Dothistroma blight ofAustrian 1967. G.W. Peterson, needle Dothistroma blight US Department of Forest of 1982. Agriculture pines. ______. Genetic responses 1999. Jr. Hamilton, and D.A. Spittlehouse, D.L. Ying, C.C. G.E., Rehfeldt,

must

toxin most

Despite

the

control

to

Columbia,

because

carcinogen.

used

low

British

been

very In

potential

be a

have

to

treatments.

therefore,

fungicides is,

considered such

is

by and

copper

workers

damaged clastogen

be spectrum

forest

and

to also

broad

risk

could mutagen

the

species; crop acceptable numerous supporting of capable are areas high-hazard species. a single for managed not are sites that ensure should managers resource in the be to available unlikely are new measures continues, research Although future. near their presence be but felled, not should trees pine areas, high-hazard In trees. leave trees). ghost as the pine treat (i.e., trees other leaving preclude not should if eating before their hands wash to workers forest for prudent is It be ingested. stands. in Dothistroma-infected working 1960s, the early since hemisphere in the southern pine radiata on Dothistroma pine, radiata Unlike Columbia. in British recommended not is this treatment its throughout susceptible remains 15, lodgepole pine age to susceptible which is Other the all) rotation. of (or most for program a spray require which would life, in high-hazard common the wild as mushrooms such resources, non-timber areas, this, a is dothistromin that shown have Studies aflatoxin. carcinogen, the potent to weak germination. and release, production, spore affect the disease to have favourable events weather in the frequency increase of a marked infection. Dothistroma of levels in unprecedented resulted infection Dothistroma of signs some 92% show revealed that northwest, province’s the plantations of percent Nine 100% mortality). almost to levels (varying low from stands, monitored In seems recovery unlikely. that defoliated so severely are 7%. close to is trees individual of mortality mortality leaf in premature resulting all needles ages of infects pine Dothistroma capacity. photosynthetic reduced and species as non-susceptible favour • If treatments, brushing or spacing conducting Dothistroma. with effective been proven have • No controls biological existing Risk to human health related closely is that dothistromin, • Dothistroma a toxin, produces needle blight needles affected. of the volume to • Wood proportional is loss yield which conditions, • Outbreaks weather on depending year to year from vary greatly • Repeated mortality. and loss lead growth to attacks severe with along lodgepole pine of plantations extensive • In Columbia, British northwest in plantations pine of 40 000 ha • Reconnaissance approximately over flights Damage and impact on productivity • Plantation maintenance Plantation • Although Management considerations (continued) considerations Management Dothistroma Needle Blight – Northern Interior Forest Region Interior Forest Blight – Northern Needle Dothistroma

JEM — Vo l u me 10 Nu m b e r 1 3 Test Your Knowledge . . .

British Columbia’s Northern Interior Forests: Dothistroma Stand Establishment Decision Aid

How well can you recall some of the main messages in the preceding Extension Note? Test your knowledge by answering the following questions. Answers are at the bottom of the page.

1. New infections are likely to be highest: a) In the fall, when it is cool and moist b) In the summer during cool dry periods c) During warm, humid conditions in the growing season

2. Only the current years’ pine needles are susceptible. a) True b) False

3. The best strategy for avoiding Dothistroma infections on dry sites is to: a) Avoid clearcutting b) Plant an exotic pine species c) Spray the area with copper fungicides d) Plant Douglas-fir e) Plant a mix of pine, spruce, and Douglas-fir

ANSWERS

e b c 3. 2. 1.

2 JEM — Vo l u me 10, Nu m b e r 1