Harvard Forest Phenology Study 1990-2006...9 0 9 2 9 9 4 96 9 8 2 0 0 0 0 2 2 0 0 4 6 YEAR NUMBER OF...

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printed by www.postersession.com From 1990 From 1990 - -2006 we observed the timing of woody vegetation development during the growing season. Bud break (50% leaf emergence) and leaf development (75% final size) on two to five permanently tagged individuals of each species are recorded at 3-7 day intervals from April through June. We have also recorded fall phenology since 1991, with the exception of 1992. Weekly observations of percent leaf coloration and percent leaf fall begin in September and continue through leaf fall. These observations have documented substantial (up to three weeks difference) interannual variation in the timing of leaf emergence (50%) and leaf development (75% final size), but good relative consistency among species and among individuals within species. In general the fall dates have shown less variability than the spring dates. Although no trend has been evident in the timing of leaf emergence and development in the spring over the course of the study, these trees have shown a trend toward later leaf senescence and leaf fall of up to five days over the course of the study. -The relative timing of observed bud break, leaf development and leaf fall were fairly consistant among individuals within a species and among means for species. -The timing of spring events among individuals within a species and among means for species exhibited about twice the range of variability observed in the timing of leaf fall. -Although spring events remain more variable there is greater consistent separation among species means in the timing of leaf fall. -Although there is a slight trend toward later leaf out, a stronger trend toward later leaf fall has resulted in a very weak trend toward an increase in “leaves on days” or growing season during the course of this study. From 1990-2006 we observed the timing of woody vegetation development during the growing season. For the first twelve years (1990-2001) we observed bud break (50% leaf emergence) and leaf development (75% final size) on two to five permanently tagged individuals of 33 woody species at 3-7 day intervals from April through June. Bud break is defined as when 50% of the buds have recognizable leaves emerging from them. Leaf development (75%) is defined as when at least 75% of the leaves have reached 75% of their final size. This point is used rather than “fully developed” because the leaves are growing rapidly during this period and it permits better estimation of a date between observations. Flowering and fruit development were also recorded if they occurred during this period. These observations documented substantial (up to three weeks difference) interannual variation in the timing of leaf emergence (50%) and leaf development (75% final size), but good relative consistency among species and among individuals within species during these twelve years. Therefore, starting in 2002 we maintained the same observation protocol, but reduced the number of species observed to nine, including red maple (Acer rubrum), sugar maple (A. saccharum), striped maple (A. pensylvanicum), yellow birch (Betula alleghaniensis), beech (Fagus grandifolia), white ash (Fraxinus americana), witch hazel (Hamamelis virginiana), white oak (Quercus alba), and red oak (Q. rubra). This subset of important, representative species allows us to continue to characterize leaf development each spring, and document inter-annual variability while reducing the time resources required for the study. We have also recorded fall phenology since 1991, with the exception of 1992. Weekly observations of percent leaf coloration and percent leaf fall begin in September and continue through leaf fall. In 2002 we reduced the species observed in the fall to fourteen, including striped maple (Acer pensylvanicum), red maple (A. rubrum), sugar maple (A. saccharum), shadbush (Amelanchier laevis), yellow birch (Betula alleghaniensis), black birch (B. lenta), paper birch (B. papyrifera), beech (Fagus grandifolia), white ash (Fraxinus americana), black gum (Nyssa sylvatica), black cherry (Prunus serotina), white oak (Quercus alba), and red oak ( ( Q. Q. rubra rubra ). ). Plant phenology is an important ecological signal integrating the atmosphere and biosphere. It responds to climate fluctuations and, especially in deciduous systems, drives seasonal changes in albedo, water transport, cloud cover and carbon exchange. Despite this importance, long-term phenological data sets are quite rare. The Harvard Forest data set is especially valuable because Harvard Forest is a Long-Term Ecological Research site with extensive historical records and current measurements of both the vegetation and atmosphere as well as carbon exchange. As part of our Schoolyard LTER program the protocols for this study have been adapted and presented for use by K-12 teachers on their school grounds. Through workshops at Harvard Forest and presentations at other environmental education workshops 20 teachers from 17 schools have begun using these protocols and submitting phenology data. Further information about our Schoolyard phenology program can be found at: http://harvardforest.fas.harvard.edu/museum/phenology.html Additional information on our research on fall phenology is available at: http:// harvardforest.fas.harvard.edu/research/leaves/autumn_leaves.html The Harvard Forest phenology data set can be accessed at: http://harvardforest.fas.harvard.edu/data/p00/hf003/hf003.html Questions about the data set can be addressed to: [email protected] Figure 1. The study is being conducted along a two kilometer loop (in red above) at the Harvard Forest (42deg 32’ 30”N and 72deg 11’ 00”W) in Petersham in north- central Massachusetts. The loop starts and ends in open areas at the Harvard Forest headquarters and is primarily in upland mixed deciduous-coniferous forest surrounding a moderate sized wetland. The elevation of the loop ranges from 335 to 365 meters and habitats range from closed forest, through forest-swamp margins to field edges. The majority of the area was agricultural land (primarily pasture) in the mid-nineteenth century. Much of the present forest is 65-85 years old following harvesting early in the twentieth century and extensive hurricane damage and salvage in 1938. Climate data is collected at a weather station located near the Harvard Forest headquarters at the southwest end of the loop and at the EMS tower approximately 1 kilometer east of the loop. SUMMARY STUDY AREA METHODS RESULTS (CONT.) OUTREACH AND DATA ACCESS INTRODUCTION Harvard Forest Phenology Study 1990-2006 John F. O’Keefe Harvard Forest, Harvard University, Petersham, MA 01366 Figure 2. In each photograph (red oak on the left and beech on Figure 2. In each photograph (red oak on the left and beech on the right) approximately two the right) approximately two - - thirds of the buds have thirds of the buds have recognizable leaves emerging, so this would represent just past recognizable leaves emerging, so this would represent just past 50% bud break in each case. 50% bud break in each case. RESULTS 100 120 140 160 180 200 220 240 260 280 300 1990 1992 1994 1996 1998 2000 2002 2004 2006 YEAR DAY OF YEAR BEAL1BB BEAL2BB BEAL3BB BEAL1L75 BEAL2L75 BEAL3L75 BEAL1LF50 BEAL2LF50 BEAL3LF50 100 120 140 160 180 200 220 240 260 280 300 320 1990 1992 1994 1996 1998 2000 2002 2004 2006 YEAR DAY OF YEAR ACRUBB BEALBB QURUBB QUALBB ACRU75 BEAL75 QURU75 QUAL75 ACRUL50 BEALL50 QURUL50 QUALL50 MEAN BUD BREAK AND 50% LEAF FALL 4 SPECIES (N=15) 110 130 150 170 190 210 230 250 270 290 310 1990 1992 1994 1996 1998 2000 2002 2004 2006 YEAR DAY OF YEAR MEANBB MEANLF50 Linear (MEANBB) Linear (MEANLF50) Figure 3. The three individuals of yellow birch show Figure 3. The three individuals of yellow birch show similar patterns in the timing of leaf development similar patterns in the timing of leaf development (BB=50% bud break and L75=75% leaf development) (BB=50% bud break and L75=75% leaf development) and leaf drop (LF50=50% leaf fall) and their timing and leaf drop (LF50=50% leaf fall) and their timing with respect to each other remains relatively similar. with respect to each other remains relatively similar. There is approximately twice as much variability in There is approximately twice as much variability in the spring events as in the fall. the spring events as in the fall. Figure 4. Just as the individuals within a species Figure 4. Just as the individuals within a species show similar patterns of leaf development and leaf show similar patterns of leaf development and leaf drop, so too do the mean patterns for each species. drop, so too do the mean patterns for each species. Four species are plotted here: red maple, yellow Four species are plotted here: red maple, yellow birch, red oak and white oak. Although the spring birch, red oak and white oak. Although the spring remains more variable there is greater consistent remains more variable there is greater consistent separation among the species in the fall. separation among the species in the fall. Figure 5. The summed mean bud break Figure 5. The summed mean bud break and leaf drop dates for the four species and leaf drop dates for the four species shown individually in Figure 4 both shown individually in Figure 4 both show a trend toward later occurrence show a trend toward later occurrence over time. However, the trend for leaf over time. However, the trend for leaf fall is greater than for bud break. fall is greater than for bud break. Figure 6. The net effect of a slightly later leaf out Figure 6. The net effect of a slightly later leaf out and a more pronounced later leaf drop during the and a more pronounced later leaf drop during the course of the study has been a slight trend toward course of the study has been a slight trend toward a longer growing season between 1991 and 2005. a longer growing season between 1991 and 2005. Figure 7. The mean 50% bud break date Figure 7. The mean 50% bud break date for all individuals continuously observed for all individuals continuously observed in the study shows a slight trend toward in the study shows a slight trend toward later leaf emergence, considerable later leaf emergence, considerable variability and, not surprisingly, does not variability and, not surprisingly, does not appear related to the date of last frost. appear related to the date of last frost. Figure 8. The mean 50% leaf fall date for Figure 8. The mean 50% leaf fall date for all individuals continuously observed in the all individuals continuously observed in the study shows a trend toward later leaf drop study shows a trend toward later leaf drop of about five days. This trend may be of about five days. This trend may be somewhat related to first frost dates, which somewhat related to first frost dates, which have trended later during the study. have trended later during the study. R R 2 =.546 =.546 R R 2= 2= .116 .116 r 2 =.054 =.054 LEAVES ON DAYS - MEAN FOR 4 SPECIES (N=15) 150 155 160 165 170 175 1990 1992 1994 1996 1998 2000 2002 2004 2006 YEAR NUMBER OF DAYS LEAVES ON DAYS Linear (LEAVES ON DAYS) R R 2 =.054 =.054 50% LEAF FALL R 2 = 0.4754 R 2 = 0.5177 250 260 270 280 290 300 1991 1993 1995 1997 1999 2001 2003 2005 YEAR DAY OF YEAR 1st frost 50% fall 5yr mean fall Linear (50% fall) Linear (1st frost) 50% BUD BREAK R 2 = 0.0429 R 2 = 0.0403 110 120 130 140 150 160 1990 1992 1994 1996 1998 2000 2002 2004 YEAR DAY OF YEAR last frost 50% BB 5 yr mean BB Linear (last frost) Linear (50% BB)

Transcript of Harvard Forest Phenology Study 1990-2006...9 0 9 2 9 9 4 96 9 8 2 0 0 0 0 2 2 0 0 4 6 YEAR NUMBER OF...

Page 1: Harvard Forest Phenology Study 1990-2006...9 0 9 2 9 9 4 96 9 8 2 0 0 0 0 2 2 0 0 4 6 YEAR NUMBER OF DAYS LEAVES ON DAYS Linear (LEAVES ON DAYS) RR2=.054=.054 50% LEAF FALL R 2 = 0.4754

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From 1990From 1990--2006 we observed the timing of woody vegetation development during the growing season. Bud break (50% leaf emergence) and leaf development (75% final size) on two to five permanently tagged individuals of each species are recorded at 3-7 day intervals from April through June. We have also recorded fall phenology since 1991, with the exception of 1992. Weekly observations of percent leaf coloration and percent leaf fall begin in September and continue through leaf fall.

These observations have documented substantial (up to three weeks difference) interannual variation in the timing of leaf emergence (50%) and leaf development (75% final size), but good relative consistency among species and among individuals within species. In general the fall dates have shown less variability than the spring dates. Although no trend has been evident in the timing of leaf emergence and development in the spring over the course of the study, these trees have shown a trend toward later leaf senescence and leaf fall of up to five days over the course of the study.

-The relative timing of observed bud break, leaf development and leaf fall were fairly consistant among individuals within a species and among means for species.

-The timing of spring events among individuals within a species and among means for species exhibited about twice the range of variability observed in the timing of leaf fall.

-Although spring events remain more variable there is greater consistent separation among species means in the timing of leaf fall.

-Although there is a slight trend toward later leaf out, a stronger trend toward later leaf fall has resulted in a very weak trend toward an increase in “leaves on days” or growing season during the course of this study.

From 1990-2006 we observed the timing of woody vegetation development during the growing season. For the first twelve years (1990-2001) we observed bud break (50% leaf emergence) and leaf development (75% final size) on two to five permanently tagged individuals of 33 woody species at 3-7 day intervals from April through June. Bud break is defined as when 50% of the buds have recognizable leaves emerging from them. Leaf development (75%) is defined as when at least 75% of the leaves have reached 75% of their final size. This point is used rather than “fully developed”because the leaves are growing rapidly during this period and it permits better estimation of a date between observations. Flowering and fruit development were also recorded if they occurred during this period.

These observations documented substantial (up to three weeks difference) interannual variation in the timing of leaf emergence (50%) and leaf development (75% final size), but good relative consistency among species and among individuals within species during these twelve years. Therefore, starting in 2002 we maintained the same observation protocol, but reduced the number of species observed to nine, including red maple (Acer rubrum), sugar maple (A. saccharum), striped maple (A. pensylvanicum), yellow birch (Betula alleghaniensis), beech (Fagus grandifolia), white ash (Fraxinus americana), witch hazel (Hamamelis virginiana), white oak (Quercus alba), and red oak (Q. rubra). This subset of important, representative species allows us to continue to characterize leaf development each spring, and document inter-annual variability while reducing the time resources required for the study.

We have also recorded fall phenology since 1991, with the exception of 1992. Weekly observations of percent leaf coloration and percent leaf fall begin in September and continue through leaf fall. In 2002 we reduced the species observed in the fall to fourteen, including striped maple (Acer pensylvanicum), red maple (A. rubrum), sugar maple (A. saccharum), shadbush (Amelanchier laevis), yellow birch (Betula alleghaniensis), black birch (B. lenta), paper birch (B. papyrifera), beech (Fagus grandifolia), white ash (Fraxinus americana), black gum (Nyssa sylvatica), black cherry (Prunus serotina), white oak (Quercus alba), and red oak ((Q. Q. rubrarubra).).Plant phenology is an important ecological signal integrating the atmosphere and

biosphere. It responds to climate fluctuations and, especially in deciduous systems, drives seasonal changes in albedo, water transport, cloud cover and carbon exchange. Despite this importance, long-term phenological data sets are quite rare. The Harvard Forest data set is especially valuable because Harvard Forest is a Long-Term Ecological Research site with extensive historical records and current measurements of both the vegetation and atmosphere as well as carbon exchange.

As part of our Schoolyard LTER program the protocols for this study have been adapted and presented for use by K-12 teachers on their school grounds. Through workshops at Harvard Forest and presentations at other environmental education workshops 20 teachers from 17 schools have begun using these protocols and submitting phenology data. Further information about our Schoolyard phenology program can be found at: http://harvardforest.fas.harvard.edu/museum/phenology.htmlAdditional information on our research on fall phenology is available at:http:// harvardforest.fas.harvard.edu/research/leaves/autumn_leaves.htmlThe Harvard Forest phenology data set can be accessed at: http://harvardforest.fas.harvard.edu/data/p00/hf003/hf003.htmlQuestions about the data set can be addressed to: [email protected]

Figure 1. The study is being conducted along a two kilometer loop (in red above) at the Harvard Forest (42deg 32’ 30”N and 72deg 11’ 00”W) in Petersham in north-central Massachusetts. The loop starts and ends in open areas at the Harvard Forest headquarters and is primarily in upland mixed deciduous-coniferous forest surrounding a moderate sized wetland. The elevation of the loop ranges from 335 to 365 meters and habitats range from closed forest, through forest-swamp margins to field edges. The majority of the area was agricultural land (primarily pasture) in the mid-nineteenth century. Much of the present forest is 65-85 years old following harvesting early in the twentieth century and extensive hurricane damage and salvage in 1938. Climate data is collected at a weather station located near the Harvard Forest headquarters at the southwest end of the loop and at the EMS tower approximately 1 kilometer east of the loop.

SUMMARY

STUDY AREA

METHODS RESULTS (CONT.)

OUTREACH AND DATA ACCESS

INTRODUCTION

Harvard Forest Phenology Study 1990-2006 John F. O’Keefe

Harvard Forest, Harvard University, Petersham, MA 01366

Figure 2. In each photograph (red oak on the left and beech on Figure 2. In each photograph (red oak on the left and beech on the right) approximately twothe right) approximately two--thirds of the buds have thirds of the buds have recognizable leaves emerging, so this would represent just past recognizable leaves emerging, so this would represent just past 50% bud break in each case.50% bud break in each case.

RESULTS

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YEAR

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Y O

F YE

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BEAL1BB

BEAL2BB

BEAL3BB

BEAL1L75

BEAL2L75

BEAL3L75

BEAL1LF50

BEAL2LF50

BEAL3LF50

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ACRUBB

BEALBB

QURUBB

QUALBB

ACRU75

BEAL75

QURU75

QUAL75

ACRUL50

BEALL50

QURUL50

QUALL50

MEAN BUD BREAK AND 50% LEAF FALL 4 SPECIES (N=15)

110130150170190210230250270290310

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MEANBBMEANLF50Linear (MEANBB)Linear (MEANLF50)

Figure 3. The three individuals of yellow birch show Figure 3. The three individuals of yellow birch show similar patterns in the timing of leaf development similar patterns in the timing of leaf development (BB=50% bud break and L75=75% leaf development) (BB=50% bud break and L75=75% leaf development) and leaf drop (LF50=50% leaf fall) and their timing and leaf drop (LF50=50% leaf fall) and their timing with respect to each other remains relatively similar. with respect to each other remains relatively similar. There is approximately twice as much variability in There is approximately twice as much variability in the spring events as in the fall.the spring events as in the fall.

Figure 4. Just as the individuals within a species Figure 4. Just as the individuals within a species show similar patterns of leaf development and leaf show similar patterns of leaf development and leaf drop, so too do the mean patterns for each species. drop, so too do the mean patterns for each species. Four species are plotted here: red maple, yellow Four species are plotted here: red maple, yellow birch, red oak and white oak. Although the spring birch, red oak and white oak. Although the spring remains more variable there is greater consistent remains more variable there is greater consistent separation among the species in the fall.separation among the species in the fall.

Figure 5. The summed mean bud break Figure 5. The summed mean bud break and leaf drop dates for the four species and leaf drop dates for the four species shown individually in Figure 4 both shown individually in Figure 4 both show a trend toward later occurrence show a trend toward later occurrence over time. However, the trend for leaf over time. However, the trend for leaf fall is greater than for bud break.fall is greater than for bud break.

Figure 6. The net effect of a slightly later leaf out Figure 6. The net effect of a slightly later leaf out and a more pronounced later leaf drop during the and a more pronounced later leaf drop during the course of the study has been a slight trend toward course of the study has been a slight trend toward a longer growing season between 1991 and 2005. a longer growing season between 1991 and 2005.

Figure 7. The mean 50% bud break date Figure 7. The mean 50% bud break date for all individuals continuously observed for all individuals continuously observed in the study shows a slight trend toward in the study shows a slight trend toward later leaf emergence, considerable later leaf emergence, considerable variability and, not surprisingly, does not variability and, not surprisingly, does not appear related to the date of last frost.appear related to the date of last frost.

Figure 8. The mean 50% leaf fall date for Figure 8. The mean 50% leaf fall date for all individuals continuously observed in the all individuals continuously observed in the study shows a trend toward later leaf drop study shows a trend toward later leaf drop of about five days. This trend may be of about five days. This trend may be somewhat related to first frost dates, which somewhat related to first frost dates, which have trended later during the study.have trended later during the study.

RR22=.546=.546

RR2=2=.116.116

rr22=.054=.054

LEAVES ON DAYS - MEAN FOR 4 SPECIES (N=15)

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LEAVES ON DAYS

Linear (LEAVES ONDAYS)

RR22=.054=.054

50% LEAF FALL

R2 = 0.4754

R2 = 0.5177

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YEA

R 1st frost50% fall5yr mean fallLinear (50% fall)Linear (1st frost)

50% BUD BREAK

R2 = 0.0429

R2 = 0.0403110

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R last frost50% BB5 yr mean BBLinear (last frost)Linear (50% BB)