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    (Campbell et al., 1990). Cate and Perkins (2003)

    reported significant correlations between CCI and

    total chlorophyll in sugar maple (Acer saccharum

    Marsh.) leaves collected during the fall colorationperiod. Chang and Robison (2003) observed strong

    relationships between CCI and foliar nitrogen in four

    hardwood species. Neilsen et al. (1995) observed

    significant correlations between CCI and foliar

    nitrogen concentration in four apple cultivars early,

    but not late, in the growing season. However, in a

    study that examined 12 red maple cultivars as a

    group, Sibley et al. (1996) found no significant

    correlations between CCI and foliar nitrogen. These

    latter two studies illustrate some limitations of chlor-

    ophyll meters. The mathematical relationships

    observed between CCI and total chlorophyll and/

    or nitrogen content vary between species (Marquard

    and Tipton, 1987; Schaper and Chacko, 1991; Shaa-

    han et al., 1999; Yamamoto et al., 2002) and within

    species during the growing season (Dwyer et al.,

    1995; Bullock and Anderson, 1998), with growth

    stage (Chapman and Barreto, 1997), with growing

    condition (Campbell et al., 1990; Simorte et al.,

    2001), and genotype (Peng et al., 1993). Thus,

    relationships must be quantified for each species

    of interest, and once determined, the relationship

    cannot be generally applied even within thatspecies.

    These limitations notwithstanding, hand-held chlor-

    ophyll meters can still be effective tools for evaluating

    forest tree species. After establishing a general corre-

    lative relationship for a particular species, it is possible

    to use a chlorophyll meter in applications for which

    precise values are not necessary. For example, rapid

    assessment of relative chlorophyll and/or nitrogen

    content in sugar maple canopies would be of particular

    utility for managers or researchers investigating sugar

    maple decline, the symptoms of which include foliarnutrient deficiencies and reduced chlorophyll content

    (Liu et al., 1997). The accuracy of a handheld chlor-

    ophyll meter in predicting chlorophyll and nitrogen

    content in growing-season sugar maple leaves has not

    been previously reported. Thus, the objective of this

    study was to establish the ability of a portable

    chlorophyll meter to estimate total chlorophyll and

    nitrogen content in large, heterogeneous samples of

    sugar maple leaves collected during the growing

    season.

    2. Materials and methods

    2.1. CCI versus nitrogen

    Samples were collected on August 17, 2001, within

    0.25 miles of the Proctor Maple Research Center

    (PMRC) in Underhill Center, VT (elevation 400 m).

    About 100 individual, visually-healthy sugar maple

    leaves were taken randomly from both understory and

    open-grown saplings and seedlings. In the case of

    seedlings, two small leaves were used to comprise

    one sample.

    Following collection, samples were placed in plas-

    tic bags and stored in a refrigerator until further

    analyses could be completed. Five chlorophyll content

    measurements were collected from each leaf with the

    CCM-200 portable chlorophyll meter (Opti-Sciences,

    Tyngsboro, MA), which calculates a unitless chloro-

    phyll content index (CCI) value from the ratio of

    optical absorbance at 655 nm to that at 940 nm. Major

    veins and areas of obvious visual damage or disease

    were avoided and all measurements were completed

    within 2 h of collection. These data yielded an average

    CCI for each leaf sample. Immediately following

    collection of CCI values, leaf samples were dried in

    an oven at 70 8C.

    Nitrogen analysis of individual leaf samples wasconducted at the Agricultural and Environmental

    Testing Laboratory of the University of Vermont

    (Burlington, VT). Dried leaf samples were ground

    in a mill to pass through a no. 20 sieve (840 mm).

    One leaf sample contained insufficient mass for reli-

    able nitrogen analysis, thereby reducing the sample

    size of the study to 99. Nitrogen content, as a percen-

    tage of dry weight (Ndw), was determined by combus-

    tion analysis with a CHN elemental analyzer (CEC

    Elemental Analyzer Model 440 with PC Compatible/

    CEC-490 Interface Unit, Leeman Labs. Inc., Lowell,MA). Simple linear regression was used to determine

    the relationship between Ndw and CCI.

    2.2. CCI versus total chlorophyll

    One-hundred healthy-appearing sugar maple leaves

    were collected from individual small trees, saplings,

    and first-year seedlings. Collections were made over

    three dates in July 2001 from sites representing a wide

    range of growing conditions, from dry to moist and

    114 A.K. van den Berg, T.D. Perkins / Forest Ecology and Management 200 (2004) 113117

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    shaded to open-grown from approximately 90400 m

    in elevation in the Champlain Valley and Green

    Mountains of Vermont. Leaf samples were placed

    in plastic bags and transported to PMRC where theywere stored in a refrigerator until the time of CCI

    measurement.

    CCI was measured using procedures described in

    the first portion of the study. Following chlorophyll

    index measurements, five 6.45 mm-diameter discs

    were collected from each leaf in the approximate

    locations of CCI measurements. Chlorophyll was

    extracted from the discs at 4 8C in the dark in a

    solution of 80% acetone (v/v). Total chlorophyll

    (chlorophyll a b) content on a leaf area basis was

    estimated with a Spectronic Genesys 8 spectrophot-

    ometer with a 10 mm light path using equations

    derived by Lichtenthaler and Wellburn (1983).

    Two obvious outliers resulting from likely transpo-

    sition errors were removed from the analysis. Simple

    linear regression was used to determine the relation-

    ship between total extractable chlorophyll and CCI.

    3. Results and discussion

    3.1. CCI versus nitrogen

    Nitrogen (Ndw) values ranged from 1.4 to 2.6%

    (Fig. 1), which are within published ranges for sugar

    maple leaf tissue from trees (Ellsworth and Liu, 1994)

    and seedlings (Ellsworth and Reich, 1992). Chloro-

    phyll content index (CCI) in the 99 samples ranged

    from 6.2 to 25.4 with a mean of 13.9 (0.43).

    The relationship between CCI and Ndw was sig-

    nificantly linear (P < 0.001). Correlation analysis

    indicates 64% of the variation in N was predicted

    by CCI (Fig. 1). Peng et al. (1993) found that most

    within-species variation in relationships between CCIand Ndw could be explained by differences in leaf

    thickness. Indeed, relationships between CCI and N

    were found to be improved by calculating specific leaf

    weight (Peng et al., 1993) or considering N on an area

    (Na), rather than dry weight, basis (Peng et al., 1995).

    Chang and Robison (2003) also found that examining

    N on an area basis improved correlation coefficients

    both within and across dates in sweetgum (Liquidam-

    bar styraciflua L.) leaves. Further study is necessary to

    examine whether the linear relationship between CCI

    and N in sugar maple leaves is improved by consider-

    ing Na, and if the relationship remains linear for maple

    leaves pooled from a wider range of collection dates

    and growing conditions. The data from this study do

    represent a relatively wide range of N values for sugar

    maple leaves (1.42.6%) collected from different light

    environments. Thus, it is probably appropriate to

    conclude that for most sugar maple leaves collectedduring the growing season, the CCM provides a

    reasonable, linear approximation of total N.

    3.2. CCI versus total chlorophyll

    Total extractable chlorophyll values from 98 sam-

    ples ranged from 0.08 to 0.47 mg/mm2 with a mean of

    0.26 (0.01). These values are within the published

    range for sugar maple leaves (Cate and Perkins, 2003).

    CCI ranged from 2.4 to 23.7 with a mean of 11.7

    (0.52).The relationship between total extractable chloro-

    phyll and CCI was significantly linear, with r2 indicat-

    ing that 76% (P < 0.001) of the variation was

    explained by a linear model (Fig. 2a). A logarithmic

    model described the relationship marginally better,

    explaining 81% of the variation (Fig. 2b). That the

    relationship had a slightly better fit following natural

    log transformations of CCI and total chlorophyll

    values is likely indicative of observations made by

    other researchers that the accuracy of portable

    Chlorophyll Content Index

    5 10 15 20 25 30

    PercentNitrogen

    1.2

    1.4

    1.6

    1.8

    2.0

    2.2

    2.4

    2.6

    2.8

    y = 0.044x + 1.403

    r2 = 0.641

    Fig. 1. Linear regression of chlorophyll content index (CCI) vs.

    total percent nitrogen (by dry weight) in 99 sugar maple leaves.

    A.K. van den Berg, T.D. Perkins / Forest Ecology and Management 200 (2004) 113117 115

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    chlorophyll meters decreases at high CCI values

    (Monje and Bugbee, 1992; Richardson et al., 2002).

    However, at least for moderate CCI values, it appears

    that the CCM is able to provide a relative estimate of

    total chlorophyll in most sugar maple leaves based on

    a linear model.

    4. Conclusions

    The data in this study indicate that the CCM is an

    effective tool for rapid and nondestructive estimation

    of relative chlorophyll and nitrogen content in sugar

    maple leaves during the growing season. Once general

    relationships are established for a particular species, it

    should be possible to use the CCM as a tool for a

    variety of management and research applications for

    which precise chlorophyll or nitrogen values are not

    required, including the assessment of relative healthstatus, the assessment of physiological changes over

    time and delineating the effects of management prac-

    tices such as fertilization.

    Acknowledgements

    This research was funded by grants from the Envir-

    onmental Protection Agency and the North American

    Maple Syrup Council.

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