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(Castanea dentata) in Ontario - Ministry of Natural Resources ...

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Recovery Strategy for the American Chestnut <strong>in</strong> <strong>Ontario</strong><br />

new American Chestnut trees. There are also ongo<strong>in</strong>g programs <strong>of</strong> habitat restoration<br />

that will benefit American Chestnut and other Carol<strong>in</strong>ian species.<br />

1.6 Threats to Survival and Recovery<br />

The follow<strong>in</strong>g threats to survival and recovery <strong>of</strong> American Chestnut are listed <strong>in</strong> order<br />

<strong>of</strong> importance:<br />

Chestnut Blight<br />

Chestnut blight is the s<strong>in</strong>gle greatest threat to American Chestnut <strong>in</strong> Canada. The blight<br />

was first noticed at the Bronx Zoo <strong>in</strong> 1904 on nursery stock, but it likely had multiple<br />

<strong>in</strong>troductions at that time. The <strong>in</strong>troduction <strong>of</strong> chestnut blight, caused by the fungus C.<br />

parasitica (Murrill) M.E. Barr, devastated the American Chestnut species throughout<br />

North America <strong>in</strong>clud<strong>in</strong>g <strong>Ontario</strong>. American Chestnut has persisted <strong>in</strong> southern <strong>Ontario</strong><br />

by resprout<strong>in</strong>g from the collars <strong>of</strong> surviv<strong>in</strong>g root systems but regenerated sprouts<br />

cont<strong>in</strong>ue to become re-<strong>in</strong>fected by the fungal pathogen. Some trees <strong>in</strong> southern <strong>Ontario</strong><br />

are not currently show<strong>in</strong>g blight symptoms. McKeen (1985) reported that 50 percent <strong>of</strong><br />

trees had no obvious blight and Melzer and Boland (2004) found 41 percent <strong>of</strong> trees to<br />

be free <strong>of</strong> disease symptoms. In the most recent survey (T<strong>in</strong>dall et al. 2004), 325 <strong>of</strong> 459<br />

trees assessed for blight (71%) had no obvious blight symptoms.<br />

Chestnut blight will cont<strong>in</strong>ue to threaten the rema<strong>in</strong><strong>in</strong>g small and isolated populations <strong>of</strong><br />

American Chestnut because it survives on sprouts and on alternative hosts.<br />

Cryphonectria parasitica has been observed to kill some alternative hosts but it usually<br />

exists on these hosts as a weak pathogen or saprophyte. Alternative hosts <strong>of</strong> C.<br />

parasitica <strong>in</strong> the Carol<strong>in</strong>ian zone <strong>of</strong> southern <strong>Ontario</strong> <strong>in</strong>clude: White Oak, Red Oak,<br />

Black Oak (Q. velut<strong>in</strong>a), Red Maple, Staghorn Sumac (Rhus typh<strong>in</strong>a), Shagbark<br />

Hickory, Bur Oak (Q. macrocarpa), Ch<strong>in</strong>quap<strong>in</strong> Oak (Q. muhlenbergii), Hop Hornbeam<br />

(Ostrya virg<strong>in</strong>iana), Blue Beech (Carp<strong>in</strong>us carol<strong>in</strong>iana), Tulip Tree (Liriodendron<br />

tulipifera) and Sassafras (Sassafras albidum) (Mooij 1997). Locations for new plant<strong>in</strong>gs<br />

<strong>of</strong> American Chestnut for restoration or nut crops should be chosen carefully as they<br />

may act as a bridge to connect diseased populations <strong>of</strong> American Chestnut to isolated<br />

populations that have escaped disease.<br />

Loss <strong>of</strong> Individuals<br />

Loss <strong>of</strong> <strong>in</strong>dividuals due to clear<strong>in</strong>g <strong>of</strong> forests for farm<strong>in</strong>g and development cont<strong>in</strong>ues to<br />

be a threat to American Chestnut <strong>in</strong> <strong>Ontario</strong>. Several sprout clumps <strong>of</strong> chestnut occur<br />

along roadsides and are repeatedly cut back or sprayed with herbicide so they will not<br />

<strong>in</strong>terfere with overhead wires. Several young trees/sprouts have been damaged or<br />

killed due to logg<strong>in</strong>g and others have been lost due to clear<strong>in</strong>g <strong>of</strong> forests and fencerows<br />

for agriculture and urban development. While many rural land owners practice good<br />

forest management and stewardship, exceptions <strong>of</strong> poorly managed forests <strong>in</strong>clud<strong>in</strong>g<br />

unsusta<strong>in</strong>able logg<strong>in</strong>g and even complete clear<strong>in</strong>g to expand other economic activities,<br />

are hav<strong>in</strong>g a negative impact.<br />

9

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