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White Pine Decline in Maine - The University of Maine - School of ...

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A Risk Map for Hemlock Woolly Adelgidrelated<br />

Damage <strong>in</strong> the Northeast.<br />

Stacy Trosper 1 , William Liv<strong>in</strong>gston 1 , Jennifer Pontius 2<br />

1 <strong>School</strong> <strong>of</strong> Forest Resources, <strong>University</strong> <strong>of</strong> Ma<strong>in</strong>e, Orono, ME, USA.<br />

2 <strong>University</strong> <strong>of</strong> Vermont, RSENR, Burl<strong>in</strong>gton, VT, USA.


Need for HWA Risk Map<br />

• Hemlock Woolly Adelgid<br />

(HWA, Adelges tsugae)<br />

<strong>in</strong>festations appeared <strong>in</strong><br />

Ma<strong>in</strong>e dur<strong>in</strong>g 2000’s<br />

• Future <strong>of</strong> hemlock<br />

uncerta<strong>in</strong><br />

• Provide some guidance<br />

on what is at risk


HWA Impacted by Cold Temperatures<br />

Hemlock Impacted by Drought<br />

Kathleen S. Shields and Carole A. S-J. Cheah.<br />

USDA Forest Service, Hamden, CT<br />

Connecticut Agricultural Experiment Station, W<strong>in</strong>dsor, CT<br />

Drought results <strong>in</strong> mortality spike<br />

Number <strong>of</strong> -25C events <strong>in</strong> Sanford, ME<br />

20<br />

190<br />

15<br />

10<br />

5<br />

Sanford<br />

180<br />

170<br />

160<br />

150<br />

0<br />

1900 1910 1920 1930 1940 1950 1960 1970 1980 1990 2000<br />

140<br />

2010


January M<strong>in</strong>imum Temperature<br />

Related to Range


Hypotheses<br />

• Cold temperatures and<br />

site factors related to<br />

drought stress<br />

determ<strong>in</strong><strong>in</strong>g factors <strong>in</strong><br />

HWA <strong>in</strong>cited decl<strong>in</strong>e<br />

• Tree r<strong>in</strong>g growth<br />

trends can be used to<br />

quantify HWA <strong>in</strong>cited<br />

decl<strong>in</strong>e


Sampl<strong>in</strong>g Plots Along Edge <strong>of</strong><br />

Infestation<br />

Calibration Plots Validation Plots<br />

Infested Non-<strong>in</strong>fest Infested<br />

Region Region Region<br />

41 (276) 7 (45) 15 (103)


• Composite score<br />

– % new growth<br />

– % transparency<br />

– % f<strong>in</strong>e twig dieback<br />

– Live crown ratio<br />

Crown Health Rat<strong>in</strong>g<br />

• Scale <strong>of</strong> 1 (no damage)<br />

to 10 (dead)<br />

• Related to % HWA<br />

<strong>in</strong>festation on twigs<br />

(r=0.87)


Quanify<strong>in</strong>g Increment Growth Trends:<br />

t-score and Percent <strong>Decl<strong>in</strong>e</strong><br />

• Percent <strong>Decl<strong>in</strong>e</strong><br />

(PD) is<br />

100 X (Initial_BAI-<br />

Narrowest_BAI)/<br />

Initial_BAI.<br />

• Related to %HWA<br />

<strong>in</strong>festation (r=0.77)<br />

• Related to CDR<br />

(r=0.86)<br />

• Not related to years<br />

<strong>of</strong> <strong>in</strong>festation<br />

(r=0.47)<br />

BAI<br />

t-score<br />

BAI<br />

(3 Year Runn<strong>in</strong>g Means)<br />

5 10 15 20 25 30<br />

-2 0 2 4 6 8 10<br />

5 10 15 20 25<br />

3 year w<strong>in</strong>dows<br />

used to calculate<br />

t-scores<br />

1985 1990 1995 2000 2005<br />

1985 1990 1995 2000 2005<br />

Bavg<br />

Tmax<br />

1985 1990 1995 2000 2005<br />

year<br />

year<br />

Bm<strong>in</strong><br />

Rmax


Decl<strong>in</strong><strong>in</strong>g Trees Require High Levels <strong>of</strong><br />

Damage


High Crown Damage Related to HWA<br />

Infestation > 10%


• Calculates probability<br />

<strong>of</strong> location be<strong>in</strong>g a<br />

decl<strong>in</strong>e site<br />

• Uses stepwise<br />

procedures<br />

• Selected<br />

– January M<strong>in</strong>imum<br />

Temperature (avg)<br />

– Slope<br />

– Hillshade<br />

Logistical Regression<br />

Predicted Actual<br />

<strong>Decl<strong>in</strong>e</strong><br />

Actual<br />

Nondecl<strong>in</strong>e<br />

Actual<br />

Total<br />

<strong>Decl<strong>in</strong>e</strong> 19.00000 1.00000 20.00000<br />

Non- 1.00000 20.00000 21.00000<br />

decl<strong>in</strong>e<br />

Predicted 20.00000 21.00000 41.00000<br />

Total<br />

Correct 0.95000 0.95238<br />

Total Correct = 0.95122%


Validation Plots<br />

• 15 plots <strong>in</strong> central<br />

Massachusetts<br />

• Percent <strong>Decl<strong>in</strong>e</strong><br />

measured<br />

• Used cluster groups<br />

from calibration plots<br />

– PD47% = <strong>Decl<strong>in</strong>e</strong><br />

Coefficients<br />

Used<br />

50 th<br />

percentile<br />

95 th<br />

percentile<br />

Logistic Model Coefficients and<br />

Prediction Success<br />

<strong>Decl<strong>in</strong>e</strong><br />

Plots<br />

Nondecl<strong>in</strong>e<br />

Plots<br />

4 (3) 6 (0) 2<br />

7 (0) 2 (4) 2<br />

Correct (Incorrect)<br />

Uncerta<strong>in</strong>


Non-decl<strong>in</strong><strong>in</strong>g hemlock stands<br />

not likely outside <strong>of</strong> blue area<br />

HWA <strong>in</strong>cited decl<strong>in</strong>e not<br />

likely <strong>in</strong> blue areas<br />

HWA Probability<br />

<strong>of</strong> <strong>Decl<strong>in</strong>e</strong>


Risk Map Consistent with Recent<br />

Observations


Thanks To:<br />

Conclusions<br />

•Northern spread <strong>of</strong> HWA will be limited by<br />

cold temperatures<br />

•Increment trends calculated as Percent<br />

<strong>Decl<strong>in</strong>e</strong> can quantify HWA damage<br />

•Hemlock grow<strong>in</strong>g on steep slopes with high<br />

solar exposure are more vulnerable to<br />

decl<strong>in</strong>e<br />

• US Forest Service STDP<br />

• Massachusetts Department <strong>of</strong> Conservation<br />

and Recreation

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