A Database of Woody Vegetation Responses to Elevated Atmospheric CO2 (NDP-072)
DOI: 10.3334/CDIAC/vrc.ndp072
Contributed by
Peter S. Curtis
Department of Evolution, Ecology, and Organismal Biology
The Ohio State University
Columbus, Ohio
Prepared by Robert M. Cushman and Antoinette L. Brenkert
Carbon Dioxide Information Analysis Center
Environmental Sciences Division
Publication No. 4888
Date Published: September 1999
Prepared for the
Environmental Sciences Division
Office of Biological and Environmental Research
Budget Activity Number KP 12 04 01 0
Prepared by the
Carbon Dioxide Information Analysis Center
OAK RIDGE NATIONAL LABORATORY
Oak Ridge, Tennessee 37831-6290
managed by
LOCKHEED MARTIN ENERGY RESEARCH CORP.
for the
U.S. DEPARTMENT OF ENERGY
under contract DE-AC05-96OR22464
Contents
1. Background Information
2. Applications of the Data
3. Data Limitations and Restrictions
4. Data Checks and Processing Performed by CDIAC
5. Instructions for Obtaining the Data and Documentation
6. References
7. Listing of Files Provided
8. Description of the Documentation File
9. Description, Format, and Partial Listings of the ASCII Data Files
10. Description aAnd Format of the Lotus 1-2-3 Binary Spreadsheet Files
11. SAS and Fortran Codes to Access the Data
Appendix A: Species Included in Database
Appendix B: Full Listing of Refs.Dat
Appendix C: Full Listing of Comments.Dat
Abstract
Curtis, P. S., R. M. Cushman, and A. L. Brenkert. 1999. A Database of Woody Vegetation Responses to Elevated Atmospheric CO2. ORNL/CDIAC-120, NDP-072. Carbon Dioxide Information Analysis Center, U.S. Department of Energy, Oak Ridge National Laboratory, Oak Ridge, Tennessee, U.S.A. doi: 10.3334/CDIAC/vrc.ndp072
To perform a statistically rigorous meta-analysis of research results on the response by woody vegetation to increased atmospheric CO2 levels, a multiparameter database of responses was compiled. Eighty-four independent CO2-enrichment studies, covering 65 species and 35 response parameters, met the necessary criteria for inclusion in the database: reporting mean response, sample size, and variance of the response (either as standard deviation or standard error). Data were retrieved from the published literature and unpublished reports.
This numeric data package contains a 29-field data set of CO2-exposure experiment responses by woody plants (as both a flat ASCII file and a spreadsheet file), files listing the references to the CO2-exposure experiments and specific comments relevant to the data in the data set, and this documentation file (which includes SAS and Fortran codes to read the ASCII data file; SAS is a registered trademark of the SAS Institute, Inc., Cary, North Carolina 27511).
NDP-072 is an enhancement of previously published CDIAC DB-1018, with additional quality control and documentation (and some corrections to the data, detailed herein).
1. Background Information
To perform a statistically rigorous synthesis of research results on the response by vegetation to increased atmospheric CO2 levels, a multiparameter database of woody-plant responses was compiled (Curtis 1996; Curtis and Wang 1998, available directly from Springer-Verlag as an abstract or complete article). Eighty-four independent CO2-enrichment studies, covering 65 species (listed in Appendix A) and 35 response parameters, met the necessary criteria for inclusion in the database: reporting mean response, sample size, and variance of the response (either as standard deviation or standard error). Data were retrieved from the published literature and in a few instances from unpublished reports. Meta-analytical methods (Cooper and Hedges 1994; Gurevitch and Hedges 1993; Gurevitch et al. 1992) have been applied to part of this database (Curtis 1996; Curtis and Wang 1998).
Physiological "acclimation" or "downward regulation" of photosynthetic rates, stomatal conductance, dark respiration, and water-use efficiency of plants exposed to elevated CO2 levels can be analyzed, keeping the following definitions in mind. "Acclimation" is in general defined as "diminishing enhancement of photosynthesis by elevated CO2 with time" (Mousseau and Saugier 1992). "Downward regulation" can be defined as "the initial stimulation of enhanced photosynthesis and growth by atmospheric enrichment eroding with time" (Idso and Kimball 1992). The phenomenon is also called "downward acclimation" (Curtis and Teeri 1992): "following prolonged exposure to high CO2, photosynthetic capacity measured at either elevated or ambient CO2 partial pressure falls to below that of plants exposed only to ambient CO2." When more than one elevated CO2 treatment level was reported, only the elevated CO2 level that was approximately twice the ambient level was included in the database. Only the longest lasting exposure experiment results on photosynthetic rates, stomatal conductance, dark respiration and water use efficiency are included, however, not multiple measurements over time from the same plant. And only responses of plants measured at elevated levels of CO2 are included for evaluation of acclimatory responses. Durations of experimental exposures are always reported.
2. Applications Of The Data
This database was produced to support a meta-analysis of the effects of elevated CO2 on woody vegetation (Curtis 1996; Curtis and Wang 1998), and it was formatted accordingly. For other applications, the user should be aware that the data may be reported in more than one unit for a given variable (e.g., for dark respiration, the data are reported in units of mg/g/d, mmol/g/h, mmol/m2/h, μmol/g/s, and μmol/m2/s; and the experimental CO2 concentrations are reported in units of cm3/m3, Pa, ppm, μbar, μl/l, and μmol/mol); this is not a problem for meta-analysis, but for other applications the user may need to convert the data to consistent units.
The effects of environmental factors (e.g., nutrient levels, light intensity, temperature), stress treatments (e.g., drought, heat, ozone, ultraviolet-B radiation), and the effects of experimental conditions (e.g., duration of CO2 exposure, pot size, type of CO2 exposure facility) on plant responses to elevated CO2 levels can be explored with this database.
3. Data Limitations and Restrictions
In many papers, the data were reported graphically, rather than numerically. In such cases, the data values reported herein were digitized from the printed figures and may therefore be less accurate.
There might also have been some confusion because of the term "standard deviation." When a "standard deviation" was reported in a published paper, it was not generally possible to verify whether this value was a sample standard deviation or the standard deviation of the mean, which is sometimes used synonymously with standard error (i.e., standard error of the mean). Unfortunately, it was not possible to settle this issue definitively without personally contacting the authors of the published papers. In all cases, where not specified or known to be otherwise, a reported standard deviation was taken to be the sample standard deviation. If this was in error, then the standard deviation, standard error, and coefficient of variation reported in this database would all be incorrect.
In some cases an error bar in a figure or confidence interval in a table was not specified as standard deviation or standard error, in which case the data contributors had to make an assumption from the error bar or confidence interval and the sample size. Instances where data were obtained by personal communication with the authors, or where standard deviation or standard error was inferred from the published data, are documented in the comments.* files (included as Appendix C). Where it was not possible to determine whether the reported variability was standard deviation or standard error, it was assumed to be standard error, for the sake of conservatism.
In some cases (e.g., in long-term exposures), duration of the CO2 exposure was approximated.
As noted in Sect. 2, various units may be used for the same parameter, so the user should apply caution in integrating observations from more than one paper. The units are reported in this database.
4. Data Checks and Processing Performed by CDIAC
An important part of the data packaging process at CDIAC involves the quality assurance (QA) of data before distribution. To guarantee data of the highest possible quality, CDIAC performs extensive QA checks, examining the data for completeness, reasonableness, and accuracy, through close cooperation with the data contributor.This database was originally published as CDIAC DB-1018, for which all entries in the data file were visually inspected for reasonableness and selected entries were spot- checked against the original publications. Additional quality-assurance and documentation was performed in the preparation of this numeric data package, and some data were corrected, as described herein.
The following describes the additional data checks that were performed in the preparation of this numeric data package and the resulting revisions to the database.
Using Excel, the spreadsheet included in the original database (db1018.xls) was converted to Lotus 1-2-3 format (ndp072.wk1). Headings were added to all columns. Lists of entries for each field were generated, to identify possible spelling variants, typographical errors, or order-of-magnitude errors in the original literature or in the compilation and data entry of the database. In fact, some variant spellings of GENUS, SPECIESP_UNIT were identified and corrected for the sake of consistency.
The definition of parameter LFTNC was corrected, from "leaf N (TNC free weight basis)" to "leaf total nonstructural carbohydrate."
The internal consistency of the reported standard errors (s.e.), standard deviations (s.d.), and sample sizes (n) was checked by calculating s.d. from the s.e. and n in DB-1018 and comparing the resulting values of s.d. with the values in DB-1018; discrepancies were resolved by checking the original publications.
The ratio of elev/amb for X, SE, SD, and N was calculated; then all observations were ranked on the basis of each ratio to identify suspect values.
The following lists the changes that were made to the original database.
- SOURCE: In entire spreadsheet, edited format of letters following T or F number to entirely lowercase.
- OBS 39 & 40 (PAP_NO 150): Corrected P_UNIT, from molH2O/m2/s to mmolH2O/m2/s.
- OBS 142 (PAP_NO 340): Replaced existing value of SD_AMB (0.9798) with value calculated from SE_AMB & N_AMB (2.4495).OBS 143 & 151 (PAP_NO 340): Corrected P_UNIT, from 0.01 g/m2 to 102 g/g.
- OBS 150 (PAP_NO 340): Replaced existing value of SD_AMB (3.9192) with value calculated from SE_AMB & N_AMB (1.9596).
- OBS 191 (PAP_NO 505): Corrected SOURCE, from F2b to F2c.
- OBS 191 (PAP_NO 505): Replaced existing values of SD_AMB (5.134) and SD_ELEV (7.7972) with values calculated from SE & N (SD_AMB = 10.268 and SD_ELEV = 3.487).
- OBS 192 (PAP_NO 505): Replaced existing values of SD_AMB (5.367), SD_ELEV (5.747), SE_AMB (2.4), SE_ELEV (2.57), N_AMB (20), and N_ELEV (20) with values provided by author: SD_AMB (5.484), SD_ELEV (4.406), SE_AMB (2.452), SE_ELEV (1.970), N_AMB (5), and N_ELEV (5).
- OBS 195 (PAP_NO 505): Corrected P_UNIT, from mgdvvt/cm3 to mgdwt/cm3.
- OBS 210 & 211 (PAP_NO 506): Corrected P_UNIT, from umol/H2O/m2/s to mol/H2O/m2/s.
- OBS 364 & 365 (PAP_NO 746): Corrected SPECIES name from tulipfera to tulipifera.
- OBS 598-599, 606-607, and 612-613 (PAP_NO 2110): Existing values for means, standard error, and standard deviation multiplied by 100, based on personal communication from author, to correct for error in the published paper (in converting from % to mg/g, data were divided by 10 rather than multiplied by 10). Personal correspondence with author also confirmed that variance values given parenthetically in Table 2 were standard deviations; the tabulated data were corrected accordingly.
To search for possible confusion between standard error and standard deviation (see Sect. 3, DATA LIMITATIONS AND RESTRICTIONS), coefficients of variation CV* (after Sokal and Rohlf 1981) were calculated for each PARAM from each mean, standard deviation, and sample size. It was expected that, for any PARAM, an anomalously low coefficient of variation for a given observation might signal that a standard error was mislabeled as a standard deviation; but no such anomalies were obvious. The database was sorted by PARAM, then by CV*_AMB and CV*_ELEV, and inspected for jumps of greater than fourfold between adjacent observations. The following lists those adjacent observations that warranted further scrutiny, along with the results of the checks:
- PARAM = BD
OBS 396, PAP_NO 2004 (CV*_AMB = 35.5828): Contacted author and verified that "mean ± SD"actually referred to sample standard deviation rather than standard error of the mean. - OBS 758, PAP_NO 2224 (CV*_AMB = 623.5): Verified tabulated value against publication.
- PARAM = BGWT
OBS 380, PAP_NO 2003 (CV*_AMB = 0) and OBS 378, PAP_NO 2003 (CV*_AMB = 2.3864): Verified tabulated values against publication. - PARAM = LFC
OBS 599, PAP_NO 2110 (CV*_AMB = 3.2753): Personal correspondence with author confirmed that variance values given parenthetically in Table 2 were standard deviations; the tabulated data were corrected accordingly. - OBS 490, PAP_NO 2043 (CV*_AMB = 16.6223): Verified tabulated value against publication.
- PARAM = LFNM
OBS 414, PAP_NO 2027 (CV*_AMB = 0.4532) and OBS 251, PAP_NO 550 (CV*_AMB = 2.3447): Verified tabulated values against publication. - PARAM = PN
OBS 513, PAP_NO 2045 (CV*_AMB = -99.0208): Verified tabulated value against publication. - OBS 638, PAP_NO 2120 (CV*_AMB = 2.6460): Based on personal communication; did not verify.
- PARAM = PN_AC
OBS 520, PAP_NO 2045 (CV*_AMB = -99.0208) and OBS 622, PAP_NO 2117 (CV*_AMB = 4.6109): Verified tabulated values against publication. - PARAM = RD_AC
OBS 589, PAP_NO 2068 (CV*_AMB = 96.7737) and OBS 162, PAP_NO 468 (CV*_AMB = 1073.9583): Verified tabulated values against publication. - PARAM = INDLA
OBS 18, PAP_NO 44 (CV*_ELEV = 10.1423) and OBS 17, PAP_NO 44 (CV*_ELEV = 43.9153): Verified tabulated values against publication. - PARAM = LFC
OBS 599, PAP_NO 2110 (CV*_ELEV = 1.9585): Personal correspondence with author confirmed that variance values given parenthetically in Table 2 were standard deviations; the tabulated data were corrected accordingly. - OBS 490, PAP_NO 2043 (CV*_ELEV = 13.8699): Corrected PARAM to LFTNC.
- PARAM = LFSTAR
OBS 151, PAP_NO 340 (CV*_ELEV = 39.3519) and OBS 143, PAP_NO 340 (CV*_ELEV = 554.3478): Verified tabulated values against publication. - PARAM = LFTNC
OBS 416, PAP_NO 2027 (CV*_ELEV = 1.2777) and OBS 773, PAP_NO 2224 (CV*_ELEV = 7.7891): Verified tabulated values against publication. - PARAM = RD_AC
OBS 589, PAP_NO 2068 (CV*_ELEV = 11.2191) and OBS 588, PAP_NO 2068 (CV*_ELEV = 129.3295): Verified tabulated values against publication. - PARAM = RGR
OBS 759, PAP_NO 2224 (CV*_ELEV = 10.8333): Verified tabulated value against publication. - OBS 406 & 407, PAP_NO 2026 (CV*_ELEV = 78.1250): The value for X_ELEV was corrected, from 0.0052 to 0.052, thereby lowering the calculated CV*_ELEV to a less anomalous 7.8125.
- OBS 192, PAP_NO 505 (CV*_ELEV = 105.7878): Tabulated data changed, as described earlier in this section, based on personal communication from author.
- PARAM = TOTN
OBS 613, PAP_NO 2110 (CV*_ELEV = 39.0833) - Personal correspondence with author confirmed that variance values given parenthetically in Table 2 were standard deviations; the tabulated data were corrected accordingly. - OBS 243, PAP_NO 521 (CV*_ELEV = 177.7945) - Error bar not labeled as to SD or SE. Assumed by data contributor to be SE, based on size of the error bars and the sample size.
5. Instructions for Obtaining the Data and Documentation
6. References
- Cooper, H., and L. V. Hedges. 1994. The Handbook of Research Synthesis. Russell Sage Foundation, New York.
- Curtis, P. S. 1996. A meta-analysis of leaf gas exchange and nitrogen in trees grown under elevated carbon dioxide. Plant, Cell and Environment 19:127- 137.
- Curtis, P. S., and J. A. Teeri. 1992. Seasonal responses of leaf gas exchange to elevated carbon dioxide in Populus grandidentata. Canadian Journal of Forest Research 22:1320-1325.
- Curtis, P. S., and X. Wang. 1998. A meta-analysis of elevated CO2 effects on woody plant mass, form, and physiology. Oecologia 113:299-313 (available directly from Springer-Verlag as an abstract or complete article).
- Gurevitch, J., and L. V. Hedges. 1993. Meta-analysis: Combining the results of independent experiments. Pp. 378-398. In S. M. Scheiner and J. Gurevitch (eds.), Design and Analysis of Ecological Experiments. Chapman and Hall, New York.
- Gurevitch, J., L. L. Morrow, A. Wallace, and J. S. Walsch. 1992. A meta- analysis of competition in field experiments. American Naturalist 140:539-572.
- Idso, S. B., and B. A. Kimball. 1992. Effects of atmospheric CO2 enrichment on photosynthesis, respiration, and growth of sour orange trees. Plant Physiology 99:341-343.
- Mousseau, M., and B. Saugier. 1992. The direct effect of increased CO2 on gas exchange and growth of forest tree species. Journal of Experimental Botany 43:1121-1130.
- Sokal, R. R., and F. J. Rohlf. 1981. Biometry. W. H. Freeman and Company, New York.
- Strain, B. R., and J. D. Cure. 1994. Direct effects of atmospheric CO2 enrichment on plants and ecosystems: An updated bibliographic data base. ORNL/CDIAC-70. Carbon Dioxide Information Analysis Center, U.S. Department of Energy, Oak Ridge National Laboratory, Oak Ridge, Tennessee.
7. Listing of Files Provided
The database consists of seven files (see Table 1), including this documentation file. The data file (ndp072.dat and ndp072.wk1), reference file (refs.dat and refs.wk1), and comment file (comments.dat and comments.wk1) are each formatted in two ways: as flat ASCII files and as binary spreadsheet files (in Lotus 1-2-3 format, but readable by other spreadsheet programs; Lotus 1-2-3 is a registered trademark of the Lotus Development Corporation, Cambridge, Massachusetts 02142).
The 29-field ndp072.dat and ndp072.wk1 files contain data (784 observations in all) relevant for CO2-exposure meta-analysis for woody plants. The ndp072.dat file can be read into SAS or Fortran programs, using the access codes provided in Sect. 11 of this numeric data package. The ndp072.dat file can also be converted into a spreadsheet file for processing, although it is simpler to use the ndp072.wk1 spreadsheet file provided in this numeric data package.
The refs.* files list the selected literature represented in the data files (84 references in all), and the comments.* files provide additional information about the studies, beyond what appears in the ndp072.* data files. The reference numbers in the refs.* and comments.* files correspond to the paper numbers in the ndp072.* data files.
8. Description of the Documentation File
ndp072.txt (File 1) - This file is an ASCII text equivalent to this document.
9. Description, Format, and Partial Listings of the ASCII Data Files
ndp072.dat (File 2)
Table 2 describes the format and contents of the ASCII data file ndp072.dat distributed with this numeric data package. This table also defines each variable, specifies units, and indicates the column in the corresponding spreadsheet file ndp072.dat in which each variable is found.
First two data records:
1 44PN umolCO2/m2/s ALNUS RUBRA
WOODYN2FIX 350 650ul/l 46 0.5GC SEED FERT HI
20mgN/l T3 11.7700 0.6400 1.4311
12.7668 5 23.2000 4.6100 10.3083 46.6539 5
2 44PN umolCO2/m2/s ALNUS RUBRA
WOODYN2FIX 350 650ul/l 46 0.5GC SEED FERT CONTROL.
T3 11.7000 1.1600 2.5938 23.2777 5
25.9000 1.4800 3.3094 13.4165 5
Last two data records:
7832224TOTWT g POPULUS TREMULOIDES
WOODYANGIO 385 642ul/l 60 6GC SEED NONE . .
F1 69.7000 2.1000 3.6373 5.6534 3
102.6000 3.6000 6.2354 6.5838 3
7842224LFSTAR% POPULUS TREMULOIDES
WOODYANGIO 385 642ul/l 60 6GC SEED NONE . .
F2 2.7600 0.1900 0.3291 12.9176 3
8.5300 0.9300 1.6108 20.4576 3
refs.dat (File 4) This ASCII file provides citations of papers included in the database. A full listing of the file is included as Appendix B.
comments.dat (File 6) This ASCII file provides experimental details from papers included in the database. A full listing of the file is included as Appendix C.
10. Description and Format of the Lotus 1-2-3 Binary Spreadsheet Files
Three Lotus 1-2-3 binary spreadsheet files (files 3, 5, and 7) contain the same information as the corresponding *.dat ASCII files 2, 4, and 6. ndp072.wk1 (File 3) This Lotus 1-2-3 binary spreadsheet file corresponds to ASCII file ndp072.dat (File 2). Table 2, which describes the contents and format of ndp072.dat, also indicates the column of ndp072.wk1 in which each variable is found. refs.wk1 (File 5) This Lotus 1-2-3 binary spreadsheet file corresponds to ASCII file refs.dat (File 4). comments.wk1 (File 7) This Lotus 1-2-3 binary spreadsheet file corresponds to ASCII file comments.dat (File 6).
11. SAS and Fortran Codes to Access the Data
The following is SAS code to read file ndp072.dat:
*SAS data retrieval routine to read ndp072.dat;
data ndp072;
infile 'ndp072.dat';
input OBSNO 1-3 @4 PAP_NO 4. @8 PARAM $char6. P_UNIT $ 14-28 GENUS $ 29-41
SPECIES $ 42-66 DIV1 $ 67-71 DIV2 $ 72-76 AMB $ 77-80 ELEV $ 81-84
CO2_UNIT $ 85-92 TIME 93-96 POT $ 97-102 METHOD $ 103-106
STOCK $ 107-114 XTRT $ 115-120 LEVEL $ 121-127 QUANT $ 128-151
SOURCE $ 152-157 X_AMB 158-167 SE_AMB 168-176 SD_AMB 177-186
CV_AMB 187-195 N_AMB 196-198 X_ELEV 199-208 SE_ELEV 209-217
SD_ELEV 218-227 CV_ELEV 228-236 N_ELEV 237-239 ;
* In the above INPUT statement, the variables CV*_AMB and CV*_ELEV have
been renamed CV_AMB and CV_ELEV, respectively.;
run;
The following is Fortran code to read file ndp072.dat:
C *** Fortran program to read the file "ndp072.dat"
C
INTEGER OBSNO, PAP_NO, N_AMB, N_ELEV, TIME
DOUBLE PRECISION X_ELEV, SD_ELEV
REAL X_AMB, SE_AMB, SD_AMB, CV_AMB, SE_ELEV, CV_ELEV
CHARACTER PARAM*6, P_UNIT*15, GENUS*13, SPECIES*25, DIV1*5,
+ DIV2*5, AMB*4, ELEV*4, CO2_UNIT*8, POT*6, METHOD*4, STOCK*8,
+ XTRT*6, LEVEL*7, QUANT*24, SOURCE*6
C
OPEN (UNIT=1, FILE='NDP072.DAT')
C
C Note that the variables CV*_AMB and CV*_ELEV have
C been renamed CV_AMB and CV_ELEV, respectively
C
10 READ (1,100,END=99) OBSNO, PAP_NO, PARAM, P_UNIT, GENUS, SPECIES,
+ DIV1, DIV2, AMB, ELEV, CO2_UNIT, TIME, POT, METHOD, STOCK, XTRT,
+ LEVEL, QUANT, SOURCE, X_AMB, SE_AMB,
+ SD_AMB,CV_AMB,N_AMB,X_ELEV,
+ SE_ELEV, SD_ELEV, CV_ELEV, N_ELEV
100 FORMAT (I3,I4,A6,A15,A13,A25,2A5,2A4,A8,A4,A6,A4,A8,A6,A7,A24,
+ A6,F9.4,1X,F8.4,1X,2(F9.4,1X),I2,3(F9.4,1X),F8.4,1X,I2)
C
GO TO 10
99 CLOSE (UNIT=1)
STOP
END
Appendix A: Species Included in Database
Acacia mangium
Acer pensylvanicum
Acer pseudoplatanus
Acer rubrum
Acer saccharinum
Acer saccharum
Alnus glutinosa
Alnus rubra
Betula alleghaniensis
Betula lenta
Betula papyrifera
Betula pendula
Betula populifolia
Betula pubescens
Brachychiton populneum
Castanea sativa
Cecropia obtusifolia
Cedrus atlantica
Citrus aurantium
Citrus sinensis
Eucalyptus microtheca
Eucalyptus polyanthemus
Eucalyptus tetrodonta
Fagus grandifolia
Fagus sylvatica
Ficus obtusifolia
Fraxinus americana
Garcinia mangostana
Gliricidia sepium
Lindera Benzoin
Liquidambar styraciflua
Liriodendron tulipifera
Malus domestica
Maranthes corymbosa
Myriocarpa longipes
Nothofagus fusca
Picea abies
Picea glauca
Picea mariana
Pinus banksiana
Pinus echinata
Pinus eldarica
Pinus nigra
Pinus ponderosa
Pinus radiata
Pinus strobus
Pinus sylvestris
Pinus taeda
Piper auritum
Poncirus trifoliata x citrusparadisi
Poncirus trifoliata x citrussinensis
Populus euramericana
Populus grandidentata
Populus interamericana
Populus tremuloides
Populus x euramericana
Pseudotsuga menziesii
Quercus alba
Quercus prinus
Quercus robur
Quercus rubra
Senna multijuga
Tabebuia rosea
Trichospermum mexicanum
Appendix B: Full Listing of refs.dat
The number at the beginning of each entry corresponds to PAP_NO, the cited paper number, as defined in Sect. 9.
44 Arnone, J.A., III, and J.C. Gordon. 1990. Effect of Nodulation, Nitrogen Fixation and CO2 Enrichment on the Physiology, Growth and Dry Mass Allocation of Seedlings of Alnus rubra Bong. New Phytologist 116:55-66. 2186 Bassow, S.L., K.D.M. McConnaughay, and F.A. Bazzaz. 1994. The Response of Temperate Tree Seedlings Grown in Elevated CO2 to Extreme Temperature Events. Ecological Applications 4(3):593-603. 2223 Bazzaz, F.A., and S.L. Miao. 1993. Successional Status, Seed Size,and Responses of Tree Seedlings to CO2, Light and Nutrients. Ecology 74(1):104-112. 2037 Bazzaz, F.A., S.L. Miao, and P.M. Wayne. 1993. CO2-induced Growth Enhancements of Co-occurring Tree Species Decline at Different Rates. Oecologia 96:478-482. 2217 Berryman, C.A., D. Eamus, and G.A. Duff. 1993. The Influence of CO2 Enrichment on Growth, Nutrient Content and Biomass Allocation of Maranthes corymbosa. Australian Journal of Botany 41:195-209. 112 Brown, K.R. 1991. Carbon Dioxide Enrichment Accelerates the Decline in Nutrient Status and Relative Growth Rate of Populus tremuloides Michx. Seedlings. Tree Physiology 8:161-173. 121 Bunce, J.A. 1992. Stomatal Conductance, Photosynthesis and Respiration of Temperate Deciduous Tree Seedlings Grown Outdoors at an Elevated Concentration of Carbon Dioxide. Plant, Cell and Environment 15:541-549. 2026 Callaway, R.M., E.H. DeLucia, E.M. Thomas, and W.H. Schlesinger. 1994. Compensatory Responses of CO2 Exchange and Biomass Allocation and their Effects on the Relative Growth Rate of Ponderosa Pine in Different CO2 and Temperature Regimes. Oecologia 98:159-166. 2043 Cipollini, M.L., B.G. Drake, and D. Whigham. 1993. Effects of ElevatedCO2 on Growth and Carbon/Nutrient Balance in the Deciduous Woody Shrub Lindera Benzoin (L.) Blume (Lauraceae). Oecologia 96:339-346. 150 Conroy, J.P., M. Kuppers, B. Kuppers, J. Virgona, and E.W.R. Barlow. 1988. The Influence of CO2 Enrichment, Phosphorus Deficiency and Water Stress on the Growth, Conductance and Water Use of Pinus radiata D. Don. Plant, Cell and Environment 11:91-98. 159 Couteaux, M.M., P. Bottner, H. Rouhier, and G. Billes. 1992. Atmospheric CO2 Increase and Plant Material Quality: Production, Nitrogen Allocation and Litter Decomposition of Sweet Chestnut. IN: Responses of Forest Ecosystems to Environmental Changes (A. Teller, P. Mathy, and J.N.R. Jeffers, eds.), Elsevier Applied Science, London, pp. 429-436. 168 Curtis, P.S., and J.A. Teeri. 1992. Seasonal Responses of Leaf Gas Exchange to Elevated Carbon Dioxide in Populus grandidentata. Canadian Journal of Forest Research 22:1320-1325. 2039 Curtis, P.S., C.S. Vogel, K.S. Pregitzer, D.R. Zak, and J.A. Teeri. 1995. Interacting Effects of Soil Fertility and Atmospheric CO2 on Leaf Area Growth and Carbon Gain Physiology in Populus x euramericana (Dode) Guinier. New Phytologist 129:253-263. 2129 Curtis, P.S., D.R. Zak, K.S. 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Avigne, L.H. Allen, and K.E. Koch. 1986. Growth of CO2-enriched Sour Orange Seedlings Treated with Gibberellins/Cytokinins. Proceedings of the Florida State Horticultural Society 99:37-39. 222 Fetcher, N., C.H. Jaeger, B.R. Strain, and N. Sionit. 1988. Long-term Elevation of Atmospheric CO2 Concentration and the Carbon Exchange Rates of Saplings of Pinus taeda L. and Liquidambar styraciflua L. Tree Physiology 4:255-262. 2041 Garcia, R.L., S.B. Idso, G.W. Wall, and B.A. Kimball. 1994. Changes in net Photosynthesis and Growth of Pinus eldarica Seedlings in Response to Atmospheric CO2 Enrichment. Plant, Cell and Environment 17:971-978. 233 Gaudillere, J.-P., and M. Mousseau. 1989. Short Term Effect of CO2 Enrichment on Leaf Development and Gas Exchange of Young Poplars (Populus euramericana cv I 214). Acta Oecologica/Oecologia Plantarum 10:95-105. 2002 Gorissen, A., P.J. Kuikman, and H. van de Beek. 1995. Carbon Allocation and water Use in Juvenile Douglas Fir under Elevated CO2. New Phytologist 129:275-282. 2036 Grulke, N.E., J.L. Hom, and S.W. Roberts. 1993. Physiological Adjustment of two Full-sib Families of Ponderosa Pine to Elevated CO2. Tree Physiology 12:391-401. 2035 Gunderson, C.A., R.J. Norby, and S.D. Wullschleger. 1993. Foliar Gas Exchange Responses of two Deciduous Hardwoods during 3 Years of Growth in Elevated CO2: no Loss of Photosynthetic Enhancement. Plant, Cell and Environment 16:797-807. 290 Hollinger, D.Y. 1987. Gas Exchange and Dry Matter Allocation Responses to Elevation of Atmospheric CO2 Concentration in Seedlings of three Tree Species. Tree Physiology 3:193-202. 314 Idso, S.B., and B.A. Kimball. 1991. Downward Regulation of Photosynthesis and Growth at High CO2 Levels. Plant Physiology 96:990-992. 318 Idso, S.B., and B.A. Kimball. 1993. Effects of Atmospheric CO2 Enrichment on Net Photosynthesis and Dark Respiration Rates of Three AustralianTree Species. Journal of Plant Physiology 141:166-171. 313 Idso, S.B., B.A. Kimball, and S.G. Allen. 1991. CO2 Enrichment of Sour Orange Trees: 2.5 Years into a Long-term Experiment. Plant, Cell and Environment 14:351-353. 322 Idso, S.B., B.A. Kimball, and S.G. Allen. 1991. Net Photosynthesis of Sour Orange Trees Maintained in Atmospheres of Ambient and Elevated CO2 Concentration. Agricultural and Forest Meteorology 54:95-101. 2123 Jarvis, P.G., H.S.J. Lee, and C.V.M. Barton. 1994. The Likely Impact of rising CO2 and Temperature on European Forests. Institute of Ecology and Resource Management, University of Edinburgh. 2045 Johnsen, K.H. 1993. Growth and Ecophysiological Responses of Black Spruce Seedlings to Elevated CO2 under Varied Water and Nutrient Additions. Canadian Journal of Forest Research 23:1033-1042. 2109 Johnson, D., D. Geisinger, R. Walker, J. Newman, J. Vose, K. Elliot, and T. Ball. 1994. Soil pCO2, Soil Respiration, and Root Activity in CO2-fumigated and Nitrogen-fertilized Pondersosa Pine. Plant and Soil 165:129-138. 340 Kaushal, P., J.M. Guehl, and G. Aussenac. 1989. Differential Growth Response to Atmospheric Carbon Dioxide Enrichment in Seedlings of Cedrus atlantica and Pinus nigra ssp. Laricio var. Corsicana. Canadian Journal of Forest Research 19:1351-1358. 362 Koch, K.E., P. Jones, W.T. Avigne, and L.H. Allen Jr. 1986. Growth, Dry Matter Partitioning, and Diurnal Activities of RuBP Carboxylase in Citrus Seedlings Maintained at Two Levels of CO2. Physiologia Plantarum 67:477-484. 2121 Kubiske, M.E., and K.S. Pregitzer. 1994. Effect of Elevated CO2 and Light Availability on the Photosynthetic Light Response of Trees of Contrasting Shade Tolerance. Tree Physiology; in press. 2120 Laboratorium Voor Plantecologie. 1992. Effect of Increased Atmospheric CO2 Concentration on Primary Productivity and Carbon Allocation in Typical Belgian Forest Ecosystems. Progress report 1992. 2028 Lavola, A., and R. Julkunen-Tiitto. 1994. The Effect of Elevated Carbon Dioxide and Fertilization on Primary and Secondary Metabolites in Birch, Betula pendula (Roth). Oecologia 99:315-321. 2165 Lewis, J.D., R.B. THomas, and B.R. Strain. 1994. Effect of Elevated CO2 on Mycorrhizal Colonization of Loblolly Pine (Pinus taeda L.) Seedlings. Plant and Soil 165:81-88. 2224 Lindroth, R.L., K.K. Kinney, and C.L. Platz. 1993. Responses of Deciduous Trees to Elevated Atmospheric CO2: Productivity, Phytochemistry, and Insect Performance. Ecology 74(3):763-777. 2065 Liu, S., and R.O. Teskey. 1995. Responses of Foliar Gas Exchange to Long-term Elevated CO2 Concentrations in Mature Loblolly Pine Trees. Tree Physiology 15:351-359. 2069 Marek, M.V., J. Kalina, and M. Matouskova. 1995. Response of Photosynthetic Carbon Assimilation of Norway Spruce Exposed to Long-term Elevation of CO2 Concentration. Photosynthetica 31:209-220. 2117 Mortensen, L.M. 1994. Effects of Carbon Dioxide Concentration on Assimilate Partitioning, Photosynthesis and Transpiration of Betula pendula Roth. and Picea abies (L.) Karst. Seedlings at two Temperatures. Acta Agriculturae Scandinavica, Section B, Soil and Plant Sciences 44:164-169. 2003 Mortensen, L.M. 1995. Effect of Carbon Dioxide Concentration on Biomass Production and Partitioning in (Betula pubescens Ehrh.) Seedlings at Different Ozone and Temperature Regimes. Environmental Pollution 87:337-343. 468 Mousseau, M. 1993. Effects of Elevated CO2 on Growth, Photosynthesis and Respiration of Sweet Chestnut (Castanea sativa Mill.). Vegetatio 104/105:413-419. 470 Mousseau, M., and H.Z. Enoch. 1989. Carbon Dioxide Enrichment Reduces Shoot Growth in Sweet Chestnut Seedlings (Castanea sativa Mill.). Plant, Cell and Environment 12:927-934. 502 Norby, R.J., C.A. Gunderson, S.D. Wullschleger, E.G. O'Neill, and M.K. McCracken. 1992. Productivity and Compensatory Responses of Yellow-poplar Trees in Elevated CO2. Nature 357:322-324. 505 Norby, R.J., and E.G. O'Neill. 1989. Growth Dynamics and Water Use of Seedlings of Quercus alba L. in CO2-enriched Atmospheres. New Phytologist 111:491-500. 506 Norby, R.J., and E.G. O'Neill. 1991. Leaf Area Compensation and Nutrient Interactions in CO2-enriched Seedlings of Yellow-poplar (Liriodendron tulipifera L.). New Phytologist 117:515-528. 503 Norby, R.J., E.G. O'Neill, W.G. Hood, and R.J. Luxmoore. 1987. Carbon Allocation, Root Exudation and Mycorrhizal Colonization of Pinus echinata Seedlings Grown under CO2 Enrichment. Tree Physiology 3:203-210. 504 Norby, R.J., E.G. O'Neill, and R.J. Luxmoore. 1986. Effects of Atmospheric CO2 Enrichment on the Growth and Mineral Nutrition of Quercus alba Seedlings in Nutrient-poor Soil. Plant Physiology 82:83-89. 2131 Norby, R.J., Wullschleger, and C.A. Gunderson. 1996. Tree Responses to Elevated CO2 and Implications for Forests. IN: Carbon Dioxide and Terrestrial Ecosystems (G.W. Koch and H.A. Mooney, eds.), Academic Press, New York, pp.1-21. 510 O'Neill, E.G., R.J. Luxmoore, and R.J. Norby. 1987. Increases in Mycorrhizal Colonization and Seedling Growth in Pinus echinata and Quercus alba in an Enriched CO2 Atmosphere. Canadian Journal of Forest Research 17:878-883. 521 Overdieck, D. 1990. Effects of Elevated CO2-concentration Levels on Nutrient Contents of Herbaceous and Woody Plants. IN: The Greenhouse Effect and Primary Productivity in European Agro-ecosystems; 5-10 April 1990; Wageningen, The Netherlands (J. Goudriaan, H. van Keulen, and H.H. van Laar, eds.), Pudoc, Wageningen, pp. 31-37. 550 Pettersson, R., and A.J.S. McDonald. 1992. Effects of Elevated Carbon Dioxide Concentration on Photosynthesis and Growth of Small Birch Plants (Betula pendula Roth.) at Optimal Nutrition. Plant, Cell and Environment 15:911-919. 2027 Pettersson, R., A.J.S. McDonald, and I. Stadenberg. 1993. Response of Small Birch Plants (Betula pendula Roth.) to Elevated CO2 and Nitrogen Supply. Plant, Cell and Environment 16:1115-1121. 553 Polle, A., T. Pfirrmann, S. Chakrabarti, and H. Rennenberg. 1993. The Effects of Enhanced Ozone and Enhanced Carbon Dioxide Concentrations on Biomass, Pigments and Antioxidative Enzymes in Spruce Seedlings. Plant, Cell and Environment 16:311-316. 2110 Pregitzer, K.S., D.R. Zak, P.S. Curtis, M.E. Kubiske, J.A. Teeri, and C.S. Vogel. 1995. Atmospheric CO2, Soil Nitrogen and Turnover of Fine Roots. New Phytologist 129(4):579-585. 582 Reekie, E.G., and F.A. Bazzaz. 1989. Competition and Patterns of Resource Use among Seedlings of Five Tropical Trees Grown at Ambient and Elevated CO2. Oecologia 79:212-222. 2046 Reid, C.D., and B.R. Strain. 1994. Effects of CO2 Enrichment on Whole-plant Carbon Budget of Seedlings of Fagus grandifolia and Acer saccharum in low Irradiance. Oecologia 98:31-39. 596 Rochefort, L., and F.A. Bazzaz. 1992. Growth Response to Elevated CO2 in Seedlings of Four Co-occurring Birch Species. Canadian Journal of Forest Research 22:1583-1587. 2038 Roth, S.K., and R.L. Lindroth. 1994. Effects of CO2-mediated Changes in Paper Birch and White Pine Chemistry on Gypsy Moth Performance. Oecologia 98:133-138. 644 Sharkey, T.D., F. Loreto, and C.F. Delwiche. 1991. High Carbon Dioxide and Sun/Shade Effects on Isoprene Emission from Oak and Aspen Tree Leaves. Plant, Cell and Environment 14:333-338. 655 Sionit, N., B.R. Strain, H. Hellmers, G.H. Riechers, and C.H. Jaeger. 1985. Long-term Atmospheric CO2 Enrichment Affects the Growth and Development of Liquidambar styraciflua and Pinus taeda Seedlings. Canadian Journal of Forest Research 15:468-471. 666 Stewart, J.D., and J. Hoddinott. 1993. Photosynthetic Acclimation to Elevated Atmospheric Carbon Dioxide and UV Irradiation in Pinus banksiana. Physiologia Plantarum 88:493-500. 2042 Sullivan, J.H., and A.H. Teramura. 1994. The Effects of UV-B Radiation on Loblolly Pine. 3. Interaction with CO2 Enhancement. 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Responses of Loblolly Pine Seedlings to Elevated CO2 and Fluctuating Water Supply. Tree Physiology 13:283-296. 2122 Vogel, C.S., and P.S. Curtis. 1995. Leaf Gas Exchange and Nitrogen Dynamics of N2-fixing, Field-grown Alnus glutinosa under Elevated Atmospheric CO2. Global Change Biology 1:55-61. 2068 Wang, K., S. Kellomaki, and K. Laitinen. 1995. Effects of Needle Age, Long-term Temperature and CO2 Treatments on the Photosynthesis of Scots Pine. Tree Physiology 15:211-218. 2152 Williams, R.S., D.E. Lincoln, and R.B. Thomas. 1994. Loblolly Pine Grown under Elevated CO2 Affects Early Instar Pine Sawfly Performance. Oecologia 98:64-71. 747 Wullschleger, S.D., and R.J. Norby. 1992. Respiratory Cost of Leaf Growth and Maintenance in White Oak Saplings Exposed to Atmospheric CO2 Enrichment. Canadian Journal of Forest Research 22:1717-1721. 746 Wullschleger, S.D., R.J. Norby, and C.A. Gunderson. 1992. Growth and Maintenance Respiration in Leaves of Liriodendron tulipifera L. Exposed to Long-term Carbon Dioxide Enrichment in the Field. New Phytologist 21:515-523. 2004 Wullschleger, S.D., R.J. Norby, and P.J. Hanson. 1995. Growth and Maintenance Respiration in Stems of Quercus alba after Four Years of CO2 Enrichment. Physiologia Plantarum 93:47-54. 7J45 Wullschleger, S.D., R.J. Norby, and D.L. Hendrix. 1992. Carbon Exchange Rates, Chlorophyll Content, and Carbohydrate Status of Two Forest Tree Species Exposed to Carbon Dioxide Enrichment. Tree Physiology 10:21-31. 2048 Yakimchuk, R., and J. Hoddinott. 1994. The Influence of Ultraviolet-B Light and Carbon Dioxide Enrichment on the Growth and Physiology of Seedlings of Three Conifer Species. Canadian Journal of Forest Research 24:1-8. 756 Ziska, L.H., K.P. Hogan, A.P. Smith, and B.G. Drake. 1991. Growth and Photosynthetic Response of Nine Tropical Species with Long-term Exposure to Elevated Carbon Dioxide. Oecologia 86:383-389.
Appendix C: Full Listing of comments.dat
The number at the beginning of each entry corresponds to PAP_NO, the cited paper number, as defined in Sect. 9.
Listed are paper numbers, authors, CO2 exposure facility, light, temperature,
watering and nutrient conditions when available, location of experimental
set-up, and comments. For the CO2 exposure facilities, watering regimes, and
locations the following distinctions were made:
CO2-exposure facilities:
BRANCH - branch chambers
GC - indoor, controlled environment: growth chambers
GH - sunlit greenhouses and chambers within greenhouses
OTC - field-based open-top chambers
SPAR - high tech soil-plant-atmosphere chambers
Watering regime:
WW - well watered
W - watered
Locations:
NA - North America
CA - Central America
AU - Australia
EU - Europe
=====================================================================
=========
44 Arnone, J.A., III, and J.C. Gordon, 1990
GC
Light: 400 umol/m2/s Photoperiod: 16h
Temperature: 26/20degC
Watering regime: WW/drip Humidity: 70%
Nutrients: daily 1/4 strength Hoagland
N Treatment: 0 vs 20 mg NH4NO3-N/l
NA: North Carolina
Root nodules from inocculation with Frankia cells
112 Brown, K.R., 1991
GC
Light: 400 umol/m2/s at canopy level Photoperiod: 18h
Temperature: 22/17degC
Watering regime: WW 6 d/wk Humidity: 45%
Macronutrients 6d/wk; N Treatment: 0.155 vs 15.5 mM NH4NO3-N
NA: Canada: Alberta
SE estimated from confidence interval
121 Bunce, J.A., 1992
GH
Light: 27-49 mol/m2/d
Temperature: 30-19degC
Watering regime: WW 2e or 3e day
fertile sandy loam+fertilizer/3 wks
NA: Maryland
SE and SD pers. comm.
150 Conroy, J.P., M. Kuppers, B. Kuppers, J. Virgona, and E.W.R. Barlow,
1988
GC
Light: 450 umol/m2/s at top of plants Photoperiod: 16h
Temperature: 25/18degC
Watering regime: daily water
nutrients added; P treatment: P levels at 4.4 vs 40 mg/pot
AU
P-deficient needles of 0.7-0.8 mgP/gdrywt or 1-1.5 mgP/gdrywt
159 Couteaux, M.M., P. Bottner, H. Rouhier, and G. Billes, 1992
GC
soil with micro flora, fauna and litter
EU: S France
Se assumed
168 Curtis, P.S., and J.A. Teeri, 1992
OTC
Temperature: local+1.5/1/2degC
Watering regime: Precip+W
available N: 2.7ug/g soil
NA: N-Michigan
183 Downton, W.J.S., W.J.R. Grant, and B.R. Loveys, 1987
GH
Light: 600-350 umol/m2/s: top of plants-pot level Photoperiod: 10h
Temperature: 25/18degC
Watering regime: WW Humidity: 60-90%
1/2 strength Hoagland 2*wk
AU
fruit dry wt
184 Downton, W.J.S., W.J.R. Grant, and E.K. Chacko, 1990
GC
Light: 450 umol/m2/s initially Photoperiod: 14-12h
Temperature: 30/22degC
Watering regime: WW daily Humidity: 50%
Oscomote each 3-4mo
AU
208 El Kohen, A., J.-Y. Pontailler, and M. Mousseau, 1991
OTC
EU: France
209 El Kohen, A., H. Rouhier, and M. Mousseau, 1992
GH
Watering regime: WW/drip
NPK Treatment: 0 NPK vs 0.82g N, 0.78gP, 0.4gK/month
EU: France
210 El Kohen, A., L. Venet, and M. Mousseau, 1993
GH
Temperature: local+-1.8degC
Watering regime: W daily
EU: France
N(#) Castanea from total # plants Castanea; from Fagus from F4
221 Ferguson, J.J., W.T. Avigne, L.H. Allen, and K.E. Koch, 1986
GH
Light: 85% from outside
Temperature: 31/23degC
Watering regime: WW
nutrients added: NPK 20:20:20; Peter's
NA: Florida
part of gibberellin and cytokinin treatment experiment
222 Fetcher, N., C.H. Jaeger, B.R. Strain, and N. Sionit, 1988
GH
Light: 1900 umol/m2/s for gas exchange measurements
Temperature controlled for 30yr average
NA: N Carolina
N(#) for stomatal conductance assumed same as for assimilation rate
233 Gaudillere, J.-P., and M. Mousseau, 1989
GC
Light: 250 umol/m2/s at top of canopy Photoperiod: 16h
Temperature: 22/15degC
Watering regime: WW Humidity: 50%
EU: France
290 Hollinger, D.Y., 1987
GC
Light: 700 umol/m2/s at top of canopy Photoperiod: 14h
Temperature: 20/10degC
Watering regime: WW Humidity: 70/90%
AU
SE of mass estimated
313 Idso, S.B., B.A. Kimball, and S.G. Allen, 1991
OTC
Watering regime: WW
nutrients added
NA: Arizona
314 Idso, S.B., and B.A. Kimball, 1991
OTC
Watering regime: WW
nutrients added
NA: Arizona
SD of mass estimated from area of F1
318 Idso, S.B., and B.A. Kimball, 1993
OTC
Watering regime: WW
nutrients added
NA: Arizona
Assimilation rate and N(#) estimated from F3
322 Idso, S.B., B.A. Kimball, and S.G. Allen, 1991
OTC
Watering regime: WW
nutrients added
NA: Arizona
340 Kaushal, P., J.M. Guehl, and G. Aussenac, 1989
GH
Light: 80% of natural outside light+160umol/m2/s at shoot level 6h/d
Temperature: local:10-23degC
Watering regime: WW Humidity: 80-90%
EU: France
SE/SD pers comm.
362 Koch, K.E., P. Jones, W.T. Avigne, and L.H. Allen Jr., 1986
GC
Light: 85% of incident light of outside
Temperature: 31/23degC
Watering regime: WW
nutrients added (Peter's)
NA: Florida
SE/SD pers comm
468 Mousseau, M., 1993
OTC
Temperature: 35-10/22-5degC
Watering regime: WW
nutrients added
EU: France
N(#) of mass assumed as in T1 pap 471
470 Mousseau, M., and H.Z. Enoch, 1989
OTC
Temperature: local+max4degC
Watering regime: WW/drip
nutrients added/yr
EU: France
502 Norby, R.J., C.A. Gunderson, S.D. Wullschleger, E.G. O'Neill, and
M.K. McCracken, 1992
OTC
soils potentially NP deficient
NA: 35.9degN 84.4degW
note on drought and nutrient deficiency
503 Norby, R.J., E.G. O'Neill, W.G. Hood, and R.J. Luxmoore, 1987
GC
Light: 540 umol/m2/s Photoperiod: 14h
Temperature: 25/7degC
Watering regime: W Humidity: 65%
soils potentially NP deficient
NA: Tennessee
potential soil nutrient deficient
504 Norby, R.J., E.G. O'Neill, and R.J. Luxmoore, 1986
GC
Light: 660 umol/m2/s at top of canopy Photoperiod: 14h
Temperature: 25/15degC
Watering regime: WW/drip Humidity: 65%
soils potentially NP deficient
NA: Tennessee
SE/SD for F1,T1,T2: e-mail; soil potentially nutrient deficient
505 Norby, R.J., and E.G. O'Neill, 1989
GH
Light: 580 umol/m2/s Photoperiod: 14h
Temperature: 26/10degC
Watering regime: WW Humidity: 65/95%
NPK treatment: 0 NPK vs 5,1.5,1.9mg N,P,K/pot/wk
NA: Tennessee
SE/SD: e-mail
506 Norby, R.J., and E.G. O'Neill,1991
GC
Light: 600 umol/m2/s Photoperiod: 14h
Temperature: 26/12deg
Watering regime: WW Humidity: 70/90%
nutrients: 20.0.4.5,16.5 mg NPK+/wk ; later 2*wk
NA: Tennessee
N(#) from author
510 O'Neill, E.G., R.J. Luxmoore, and R.J. Norby, 1987
GC
Light: 450 umol/m2/s Photoperiod: 14h
Temperature: 26/10degC
Watering regime: WW
no nutrients added
NA: Tennessee
521 Overdieck, D., 1990
GC
Watering regime: W as precip
soils of average fertility
EU: Germany: 52degN 8degE
550 Pettersson, R., and A.J.S. McDonald, 1992
GC
Light: 600 umol/m2/s Photoperiod: 18h
Temperature: 20degC
hydroponics Humidity: 45%
nutrient solution
EU: Sweden
N(#) 2-5: pers comm for gas exchange; as T1 for other measures
553 Polle, A., T. Pfirrmann, S. Chakrabarti, and H. Rennenberg, 1993
GC
controlled as for local environment
Watering regime: WW:drip acidic mists
Ozone Treatment: 0.02 vs 0.08 cm3/m3: 24hrs/d like higher elevations
EU: Germany:Bavaria
582 Reekie, E.G., and F.A. Bazzaz, 1989
GH
Light: local with 1000-1200 umol/m2/s max levels
Temperature: local 30/27degC
Watering regime: WW
monthly Peter's fertilization(20:20:20)
Plant competition of tropical plants
NA: Massachusetts
596 Rochefort, L., and F.A. Bazzaz, 1992
GH
Light: 900 umol/m2/s clear days
Temperature: 28/20degC
Watering regime: WW Humidity: 73%
nutrients added each 2 weeks
NA: Massachusetts
644 Sharkey, T.D., F. Loreto, and C.F. Delwiche, 1991
GH
Light: 300-500 umol/m2/s (gas measurements at 900 umol/m2/s)
Photoperiod: 15h
Temperature: 25/20degC Humidity: 70%/85%
NA: Wisconsin
Partly a shading and isoprene emission experiment
655 Sionit, N., B.R. Strain, H. Hellmers, G.H. Riechers, and C.H. Jaeger,
1985
GH
Temperature: night temp controlled
Watering regime: WW/drip Humidity: 70%
nutrients (Hoagland 1/15 strength daily
NA: North Carolina
666 Stewart, J.D., and J. Hoddinott, 1993
GH
Light: 600 umol/m2/s as maximum Photoperiod: 18h
Temperature: 15-32degC (local)
Watering regime: WW:2*wk
nutrients 1/wk
UVB Treatment: 0.005-0.03 vs 0.25-0.90 W/m2
NA: Canada: Alberta
676 Surano, K.A., P.F. Daley, J.L.J. Houpis, J.H. Shinn, J.A. Helms,
R.J. Palassou, and M.P. Costella, 1986
OTC
Light: 80-90% from outside
Temperature: local+upto5degC
Watering regime: WW:3*wk+ Humidity: down to 10%
nutrients added/month: NPK + 2.2,1.8,1.3 g/pot/month
NA: California
682 Thomas, R.B., D.D. Richter, H. Ye, P.R. Heine, and B.R. Strain, 1991i
GC
Light: 1000 umol/m2/s Photoperiod: 14h
Temperature: 29/23degC
Watering regime: WW Humidity: 70%
nutrients added daily with/without N
N Treatment: 0 vs 7.0 mM NH4NO3-N
NA: South Carolina
Seeds inocculated with Rhizobium
745 Wullschleger, S.D., R.J. Norby, and D.L. Hendrix, 1992
OTC
gas exchange measures at 1300 umol/m2/s
NA: 35.9degN 84.4degW
Precip 169 cm at study site compared to 139 cm as 30 yr average
746 Wullschleger, S.D., R.J. Norby, and C.A. Gunderson, 1992
OTC
NA: 35.9degN 84.4degW
747 Wullschleger, S.D., and R.J. Norby, 1992
OTC
NA: 35.9degN 84.4degW
756 Ziska, L.H., K.P. Hogan, A.P. Smith, and B.G. Drake, 1991
OTC
Light: 740 umol/m2/s average; 1200umol/m2/s max Photoperiod: 10h
Temperature: 36.5/21.2degC
Watering regime: WW 2*day Humidity: 60%/85%
nutrients added (Osmocote)
CA: 83.9degN 9.2degW
Values differ slightly from Table: pers comm
2002 Gorissen, A., P.J. Kuikman, and H. Van De Beek, 1995
GC
Light: 400 umol/m2/s Photoperiod: 16h
Temperature: 18/14degC
Watering regime: W Humidity: 70-80%
EU: 52.2degN 5.8degE
2003 Mortensen, L.M., 1995
GC
Light: 18 mol/m2/day for temp treatment
Light: 22 mol/m2/day for Ozone treatment Photoperiod: 24h
Temperature: 17.3degC=control
Watering regime: WW
nutrients added
2 Treatments: Ozone: 7 vs 62 nmol/mol for 8 hrs
Temperature: 15.3 vs 20 degC
EU: 60.8degN 11.5degE
2004 Wullschleger, S.D., R.J. Norby, and P.J. Hanson, 1995
OTC
NA: 35.9degN 84.4degW
Pisolithus tinctorius mycorrhizal inoculum; stem respiration
2005 Teskey, R.O., 1995
BRANCH
Light: 1200 umol/m2/s for gas exchange measurements
Watering regime: irrigated
NA: Georgia: 33.9degN 82.3degW
2026 Callaway, R.M., E.H. DeLucia, E.M. Thomas, and W.H. Schlesinger, 1994
GC
Light: 1000 umol/m2/s Photoperiod: 12h
Temperature Treatment: 25/10degC vs 30/25degC
Watering regime: WW Humidity: 45%i during day
nutrients 1/2 strength Hoagland
NA: Nevada
2027 Pettersson, R., A.J.S. McDonald, and I. Stadenberg, 1993
GC
Light: 600 umol/m2/s Photoperiod: 18h
Temperature: 20degC
Hydroponic Humidity: 50%
nutrient solution
N Treatment: 0.07 vs 0.15 molN/molN/d
EU: Sweden
2028 Lavola, A., and R. Julkunen-Tiitto, 1994
GH
Light: local -- 1137-175 umol/m2/s
Temperature: 22/15degC
NKP Treatment: 0 vs 500 kg/ha
EU: Finland
2032 Tschaplinski, T.J., R.J. Norby, and S.D. Wullschleger, 1993
GC
Light: 720 umol/m2/s Photoperiod: 14h
Temperature: 26/16degC
H2O Treatment: weekly vs biweekly watering Humidity: 85-90%
fertilized/month (Peter's NPK 20:20:20)
NA: Tennessee
2035 Gunderson, C.A., R.J. Norby, and S.D. Wullschleger, 1993
OTC
Light: 1100-2300 umol/m2/s for gas exchange measurements
Temperature: local
Watering regime: precip
NA: 35.9degN 84.4degW
2036 Grulke, N.E., J.L. Hom, and S.W. Roberts, 1993
GC
Light: 713 umol/m2/s at canopy height Photoperiod: 12hr later 14h
Temperature: 25/19degC
Watering regime: WW Humidity: 46-57%/81%
fertilized weekly
NA: California
2037 Bazzaz, F.A., S.L. Miao, and P.M. Wayne, 1993
GH
Light: 37% and 75 % of full sun
Temperature: 30/23degC
2 Treatments: Light: 37% and 75% of full sun
Fertilizer: 0.18 and 1.8 g Oscomote
NA: Massachusetts
2038 Roth, S.K., and R.L. Lindroth, 1994
GC
Light: 501 umol/m2/s Photoperiod: 15h
Temperature: 25/20degC
Watering regime: WW/drip Humidity: 70/85%
fertilized 1/2 strength Hoagland 2*per day
NA: Wisconsin
2039 Curtis, P.S., C.S. Vogel, K.S. Pregitzer, D.R. Zak, and J.A. Teeri, 1995
OTC
Light: gas exchange measures at 1800 umol/m2/s
Temperature: local
Watering regime: WW
Soil Treatment: 45 vs 346 ug N/g/d N mineralization in soils
64 vs 110 mg extractable PO4/kg soil
NA: N-Michigan
2041 Garcia, R.L., S.B. Idso, G.W. Wall, and B.A. Kimball, 1994
OTC
Watering regime: WW
fertilized
NA: Arizona
2042 Sullivan, J.H., and A.H. Teramura, 1994
GH
Light: ~80-85% of outdoors
Temperature: 27/23degC
Watering regime: WW/daily
fertilized 1/2 strength Hoagland
UVB Treatment: 8 hrs daily 8.8 vs 13.8 kJ/m2
NA: Maryland
SE for T1 SE for F1 (e-mail)
2043 Cipollini, M.L., B.G. Drake, and D. Whigham, 1993
OTC
Light: 10-100-occasionally 1000 umol/m2/min
NA: Maryland
2044 Tissue, D.T., R.B. Thomas, and B.R. Strain, 1993
OTC
Watering regime: precip
1/2 strength Hoagland 2*week
2 Treatments: High NP:7mol/m2 NH4NO3+1mol/m3 PO4;
low P:same N+0.2mol/m3P;
lowN:1mol/m3NH4NO3+1mol/m3PO4
NA: North Carolina
N(#) in T1 does not match text
2045 Johnsen, K.H., 1993
GC
Light: 450 umol/m2/s at bench height Photoperiod: 19h
Temperature: 20/15degC
watering treatment Humidity: 70/90%
treatment within 1/3 strength Ingestad
2 Treatments:
WW vs drought cycles (fertilized with 8 mL 300 ppmN: Ingestad);
Fertilization: 6 mL/wk then 12 mL after 71 days vs 12mL,
18 mL, 24 mL, 32 mL after day 1, 42, 71 and 104
NA: Canada: Ontario
2046 Reid, C.D., and B.R. Strain, 1994
GC
Light: 65 umol/m2/s Photoperiod: 12h
Temperature: 19/15degC
Watering regime: WW daily
1/4 strength Hoagland
NA: North Carolina
2047 Eamus, D., C.A. Berryman, and G.A. Duff, 1993
OTC
Light: ambient local
Temperature: local-up to 1.5degC
AU
2048 Yakimchuk, R., and J. Hoddinott, 1994
GC
Light: 150 umol/m2/s+2hrs 40 umol/m2/s Photoperiod: 18h
Temperature: 20/18degC
Watering regime: WW Humidity: 65%
fertilized weekly
Ozone treatment: 1.1 uW/cm2 vs 150 uW/cm2 8hrs/day
NA: Canada: Alberta
potsize: pers. com.
2065 Liu, S., and R.O. Teskey, 1995
BRANCH
Light: gas exchange at 1000-2000 umol/m2/s
Temperature: 16.5degC
Watering regime: W+precip
low to medium soil fertility
NA: 33.9degN 83.3degW
mature trees, low fertility site
2068 Wang, K., S. Kellomaki, and K. Laitinen, 1995
OTC
Temperature treatment: ambient vs hot=amb+2degC in summer,amb+5-20degC
Watering regime: W+precip
sandy soil
EU: 62.8degN 30.9degE
chamber around coniferous saplings; elevated CO2 only during daytime
2069 Marek, M.V., J. Kalina, and M. Matouskova, 1995
OTC
native Coniferous
EU: 49.5degN 18.5degW
native coniferous; elevated CO2 level is saturating level
2070 Eamus, D., G.A. Duff, and C.A. Berryman, 1995
SPAR
Light: 68% of full
Temperature: local minus upto 3degC
Watering regime: WW/drip
Osmocote in soils
AU
2071 Eamus, D., C.A. Berryman, and G.A. Duff, 1995
SPAR
Light: 66% of full
Temperature: local minus upto 3degC
Watering regime: WW 2*day
fertilized each 2 weeks
AU
2109 Johnson, D., D. Geisinger, R. Walker, J. Newman, J. Vose, K. Elliot,
and T. Ball, 1994
OTC
Watering regime: WW
N treatment: 0 vs 20 g/m2/yr ammonium sulfate
NA: California
SE vs SD estimates F5; chamber description in Ball et al (1992)
2110 Pregitzer, K.S., D.R. Zak, P.S. Curtis, M.E. Kubiske, J.A. Teeri,
and C.S. Vogel, 1995
OTC
Watering regime: WW
Soil treatment: 45 vs 348 ug N/g/d N mineralization in soils;
64 vs 110 mg extractable PO4/kg soil
NA: N-Michigan
2117 Mortensen, L.M., 1994
GC
Light treatment: 15 mol/m2/d then 22 mol/m2/d for birch,
21 mol/m2/d for spruce
Photoperiod: 24h
Temperature Treatment: 15.3 vs 20.0 degC
Watering regime: WW 600 vs 1000 Pa as wvpd at 15.3 vs 20degC
fertilized, see Mortensen, 1994
EU: Norway
2120 Laboratorium Voor Plantecologie 1992
GC
Light: 270umol/m2/s Photoperiod: 16h
Temperature: 22/17.5degC
Watering regime: WW/drip Humidity: 65%
fertilized at optimal levels
EU: Belgium
2121 Kubiske, M.E., and K.S. Pregitzer, 1994
OTC
Light Treatment: low and high; understory imitation
NA: N-Michigan
2122 Vogel, C.S., and P.S. Curtis, 1995
OTC
Temperature: local+2.6degC
fertilized with 4.5 g/m2 N
NA: 45.6degN 84.7degW
nodule inoculations
2123 Jarvis, P.G., H.S.J. Lee, and C.V.M. Barton, 1994
OTC
Light and temperature not reported for growth
EU: Scotland
N(#) pers comm for T2
2129 Curtis, P.S., D.R. Zak, K.S. Pregitzer, and J.A. Teeri, 1994
OTC
Temperature: local+3degC
Watering regime: precip+W
All rootboxes received 4.5 g/m2 N; similar to natural dry oak forest
NA: N-Michigan
2131 Norby, R.J., Wullschleger, and C.A. Gunderson, 1996
OTC
NA: Tennessee
Sample size and SD from pers comm.
2152 Williams, R.S., D.E. Lincolm, and R.B. Thomas, 1994
OTC
Watering regime: precip+W
modified Hoagland 7mmol NH4NO3+1mmolPO4 /wk
NA: North Carolina
2165 Lewis, J.D., R.B. Thomas, and B.R. Strain, 1994
GH
Temperature: 28/17 - 28/22degC
Watering regime: WW
1/2 strength Hoagland/wk; P Treatment: 0.083mM KH2PO4 vs 0.5mM KH2PO4:
P stress
NA: North Carolina
inocculation Pisolithus tinctorius vs not
2186 Bassow, S.L., K.D.M. McConnaughay, and F.A. Bazzaz, 1994
GH
Light: natural+supplement when light<500umol/m2/s i
Photoperiod local: 6-19h
Temperature: 28/22degC
Fertilizer Treatment: 0.12 vs 1.2 g Osmocote > N input of
40 vs 400 kg N/ha/yr; 3 mo after initial Osmocote
weekly 200 ml Peter's solution (20:20:20) at
0.042 v s 0.42 g/l/wk
NA: Massachusetts
N(#) F1: pers. comm
2217 Berryman, C.A., D. Eamus, and G.A. Duff, 1993
OTC
Light: 65% of full
Temperature: 29.7degC
Watering regime: WW:3*day
nutrients added; also 5 g low P Osmocote
AU
2223 Bazzaz, F.A., and S.L. Miao, 1993
GH
Light treatment: full gap light vs 37% thereof
Temperature: 27/20 > 30/23degC
Watering regime: WW
nutrient treatment: N equivalents of 40 vs 400 kg N/ha/yr i.e.
0.18 vs 1.8 g Osmocote/pot
NA: Massachusetts
2224 Lindroth, R.L., K.K. Kinney, and C.L. Platz, 1993
GH
Light: 490 mol/m2/s 70cm above pots Photoperiod: 15h
Temperature: 25/20degC
Watering regime: WW/drip Humidity: 70/80%
1/2 strength Hoagland
NA: Wisconsin
native mycorrhiza in soil

