SP017: Influence of tree-fall gaps on soil characteristics in gaps of varying sizes in the Andrews Experimental Forest, 1995
Notice
"As Is" Basis: All content, including maps and forecasts, is provided without warranties. Users are advised to independently verify critical information.
Citation
Griffiths, R. 2011. Influence of tree-fall gaps on soil characteristics in gaps of varying sizes in the Andrews Experimental Forest, 1995 Long-Term Ecological Research Andrews Forest LTER Site. [Database]. Available: https://andrewsforest-stage.forestry.oregonstate.edu/data/fsdb-data-catalog/SP017 Accessed 2026-05-10.
Abstract
This is the first of three tree-fall gap studies conducted at the H.J. Andrews Experimental Forest addressing the effects of tree-fall gaps on forest soil characteristics. The second (Gap2) compared the effects of gaps on soil properties along both N-S and E-W transects to better differentiate between microclimate and vegetation effects within gaps. The final study (Gap3) expanded the number of variables studied and sampling intensity. By using the same grid system as Dr. Andy Gray in his vegetation survey work, the Gap3 study provided the most definitive connection between above-ground vegetation and associated below-ground processes. Soil properties in 10, 20, 30, and 50 meter tree-fall gaps were compared with soils in the surrounding old-growth Douglas-fir forest by sampling at 1 meter intervals along transects running north and south through the gaps. These transects extended one radius into the surrounding forest. This study was designed to determine if carbon cycling within these gaps were different from those in the soils of surrounding undisturbed forests. If there were differences, she wanted to determine what sized gap was required to show an effect. These transects were divided into four zones. Two zones were north of the E-W centerline; one in and one out of the gap. The other two zones were south of the E-W centerline; one in and one out of the gap.
Coverage
Temporal coverage: 1995-01-07 to 1995-01-08
Geographic coverage: N/A
Bounds: W N/A, E N/A, N N/A, S N/A
Purpose
- Tree-fall gaps are known to play an important role in the formation and maintenance of old-growth forest structure and forest biodiversity. Prior research has focused on above-ground vegetative succession and population dynamics and little is known about changes occurring below-ground as vegetation becomes reestablished. The interplay between gap microclimatic gradients and both vegetation and the below-ground component of the ecosystem is potentially complex. Thus to understand how gaps influence forest floor carbon cycling, one must consider both above and below-ground components.
- Soil moisture and temperature were both higher in the gap than in the surrounding forest but SOM, lab respiration and litter depth were both lower in the gap than in the forest. These results suggest that either litter input is lower in the gap than in the surrounding forest and/or that the decomposition rates are lower in the gap. Except for the smallest gap, soil moisture was lower and temperature higher in the northern half of the gap. In the 50 m gaps, laboratory respiration rates, litter depth, and soil organic matter (SOM) were higher in the southern portion of the gap as were total carbon values.
Project
Title: Long-Term Ecological Research
Personnel
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Sherri L. Johnson - Principal Investigator US Forest Service ;Pacific NW Research Station ;3200 SW Jefferson Way, Corvallis, OR, 97331, USAPhone: 541-758-7771Email: sherri.johnson2@usda.gov, sherri.johnson@oregonstate.edu
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Julia A. Jones - Principal Investigator Oregon State University;Department of Geosciences; Wilkinson Hall 104, Corvallis, OR, 97331-5506, USAPhone: (541) 737-1224Email: Julia.Jones@oregonstate.edu, geojulia@comcast.netORCID: http://orcid.org/0000-0001-9429-8925
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Matthew G Betts - Principal Investigator Department of Forest Ecosystems and Society; 201E Richardson Hall; College of Forestry; Oregon State University, Corvallis, OR, 97331Phone: (541) 737-3841Email: matt.betts@oregonstate.edu
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Michael P. Nelson - Principal Investigator Department of Forest Ecosystems and Society; 201K Richarson Hall; College of Forestry; Oregon State University, Corvallis, OR, 97331Phone: 541-737-9221Email: mpnelson@oregonstate.eduORCID: http://orcid.org/0000-0001-6917-4752
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David Bell - Principal Investigator Email: david.bell@usda.gov, david.bell@oregonstate.edu
Abstract
- The H.J. Andrews Experimental Forest is a living laboratory that provides unparalleled opportunities for the study of forest and stream ecosystems in the central Cascade Range of Oregon. Since 1980, as a part of the National Science Foundation Long Term Ecological Research (NSF-LTER) program, the Andrews Experimental Forest has become a leader in the analysis of forest and stream ecosystem dynamics.
- Long-term field experiments and measurement programs have focused on climate dynamics, streamflow, water quality, and vegetation succession. Currently researchers are working to develop concepts and tools needed to predict effects of natural disturbance, land use, and climate change on ecosystem structure, function, and species composition.
- The Andrews Experimental Forest is administered cooperatively by the USDA Forest Service Pacific Northwest Research Station, Oregon State University and the Willamette National Forest. Funding for the research program comes from the National Science Foundation (NSF), US Forest Service Pacific Northwest Research Station, Oregon State University, and other sources.
Funding
Data were provided by the HJ Andrews Experimental Forest research program, funded by the National Science Foundation's Long-Term Ecological Research Program (DEB 2025755), US Forest Service Pacific Northwest Research Station, and Oregon State University. National Science Foundation: DEB1440409
Study Area Description
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Long-Term Ecological Research The Andrews Forest is situated in the western Cascade Range of Oregon, and covers the entire 15,800-acre (6400-ha) drainage basin of Lookout Creek. Elevation ranges from 1350 to 5340 feet (410 to 1630 m). Broadly representative of the rugged mountainous landscape of the Pacific Northwest, the Andrews Forest contains excellent examples of the region's conifer forests and associated wildlife and stream ecosystems. These forests are among the tallest and most productive in the world, with tree heights of often greater than 250 ft (75 m). Streams are steep, cold and clean, providing habitat for numerous aquatic organisms.
Associated Party
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Robert P. Griffiths
Role: Principal InvestigatorOregon State University;Dept. of Forest Science;321 Richardson Hall, Corvallis, OR, 97331-5752, USAPhone: (541) 737-6559Email: bbgriff@peak.org, griff@for.orst.edu
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Robert P. Griffiths
Role: AbstractorOregon State University;Dept. of Forest Science;321 Richardson Hall, Corvallis, OR, 97331-5752, USAPhone: (541) 737-6559Email: bbgriff@peak.org, griff@for.orst.edu
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Robert P. Griffiths
Role: CreatorOregon State University;Dept. of Forest Science;321 Richardson Hall, Corvallis, OR, 97331-5752, USAPhone: (541) 737-6559Email: bbgriff@peak.org, griff@for.orst.edu
Contact
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Information Manager
Andrews Forest LTER Program, US Forest Service Pacific Northwest Research Station, 3200 SW Jefferson Way, Corvallis, OR, 97331Email: hjaweb@fsl.orst.edu
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Robert P. Griffiths
Oregon State University;Dept. of Forest Science;321 Richardson Hall, Corvallis, OR, 97331-5752, USAPhone: (541) 737-6559Email: bbgriff@peak.org, griff@for.orst.edu
Publisher
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Andrews Forest LTER Site
Role: PublisherForest Ecosystems and Society Department in Forestry, Oregon State University, 201K Richardson Hall, Corvallis, OR, 97331-5752Phone: (541) 737-8480Email: lterweb@fsl.orst.edu
Study Description
This is the first of three tree-fall gap studies conducted at the H.J. Andrews Experimental Forest addressing the effects of tree-fall gaps on forest soil characteristics. The second (Gap2) compared the effects of gaps on soil properties along both N-S and E-W transects to better differentiate between microclimate and vegetation effects within gaps. The final study (Gap3) expanded the number of variables studied and sampling intensity. By using the same grid system as Dr. Andy Gray in his vegetation survey work, the Gap3 study provided the most definitive connection between above-ground vegetation and associated below-ground processes. Soil properties in 10, 20, 30, and 50 meter tree-fall gaps were compared with soils in the surrounding old-growth Douglas-fir forest by sampling at 1 meter intervals along transects running north and south through the gaps. These transects extended one radius into the surrounding forest. This study was designed to determine if carbon cycling within these gaps were different from those in the soils of surrounding undisturbed forests. If there were differences, she wanted to determine what sized gap was required to show an effect. These transects were divided into four zones. Two zones were north of the E-W centerline; one in and one out of the gap. The other two zones were south of the E-W centerline; one in and one out of the gap. Tree-fall gaps are known to play an important role in the formation and maintenance of old-growth forest structure and forest biodiversity. Prior research has focused on above-ground vegetative succession and population dynamics and little is known about changes occurring below-ground as vegetation becomes reestablished. The interplay between gap microclimatic gradients and both vegetation and the below-ground component of the ecosystem is potentially complex. Thus to understand how gaps influence forest floor carbon cycling, one must consider both above and below-ground components. Field Methods - SP017
Purpose: Tree-fall gaps are known to play an important role in the formation and maintenance of old-growth forest structure and forest biodiversity. Prior research has focused on above-ground vegetative succession and population dynamics and little is known about changes occurring below-ground as vegetation becomes reestablished. The interplay between gap microclimatic gradients and both vegetation and the below-ground component of the ecosystem is potentially complex. Thus to understand how gaps influence forest floor carbon cycling, one must consider both above and below-ground components.
Methods
Method Steps
Field Methods - SP017
- Litter depth and soil temperature measurements were made in the field.
- Litter depth was measured with a cm ruler and soil temperatures were made in the top 10 cm of soil using a dial thermometer calibrated with ice water. Cores (4.7 x 10 cm) were collected for bulk density measurements. Grab samples were taken to a depth of 10 cm with a trowel for soil for the laboratory measurements of gravimetric soil moisture, laboratory respiration and total N and C.
Laboratory Methods - SP017
- In preparation for laboratory analyses, all soils were sieved through a 2-mm sieve. Soil moisture was determined by drying duplicate 10 g field-moist sieved soils at 100°C for at least 8 h. The percent soil moisture was calculated by dividing the difference between wet and dry samples and dividing that number by the dry wt., which was then multiplied by 100. Soil organic mater (SOM) was measured as weight loss after ignition at 550 ºC for 12 h on soils that had been dried at 100°C for 12 h.
- Laboratory respiration measurements were made in duplicate on 5 g of field-moist soil brought up to a moisture level of 75% with de-ionized water. The soil sample was added to a 25-mL Erlenmeyer flask. Once sealed with serum bottle stoppers, the flasks were incubated at 15°C for 2 weeks. Headspace CO concentration was measured using a gas chromatograph fitted a flame ionization detector and a methanizer in series.
- Ten percent of the samples were analyzed for total carbon and nitrogen using a Carlo-Erba® NA Series 2 CNS analyzer. The soils were pulverized and passed through a 60 mesh screen in preparation for analysis. Sample size varied from 8-15 mg.
Sampling
Study Extent
- Sampling frequency: 1 set of measurements at each sample node on grid
Sampling Description
- A general description of these gaps and the rational for this long-term study have been described by Gray and Spies (1996). The experimental design and site descriptions have been published (Gray and Spies, 1996, 1997) but are summarized below.
- Replicate 10, 20, 30 and 50 gaps as well as one 30 m control gap were used to determine how tree-fall gaps influence soil carbon cycling. These gaps were created in the fall of 1990 at a site located 44 15N, 122 15W at an elevation of 900 m at the H.J. Andrews Experimental Forest in the Central Oregon Cascade Mountains. This study was conducted 5 years after gap formation. North-south transects were established through the center of all gaps and sample nodes were located at 1 m intervals along those transects. These transects ran one radius length into the surrounding forest. These transects were divided into four zones. Two zones were north of the E-W centerline; one in and one out of the gap. The other two zones were south of the E-W centerline; one in and one out of the gap.
- Citation:
- Gray, A.N., and T.A. Spies. 1996. Gap size, within-gap position, and canopy structure effects on seedling establishment of conifer species in forest canopy gaps. Journal of Ecology 84: 635-645.
- Gray, A.N., and T.A. Spies. 1997. Microsite controls on tree seedling establishment in conifer forest canopy gaps. Ecology 78:2458-2473.
Spatial Sampling Units
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Andrews Experimental Forest (HJA)
W -122.26172200, E -122.10084700, N 44.28196400, S 44.19770400Altitude: 1631 to 1631 meter
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Cascade Head Experimental Forest
W -123.99172777, E -123.89730000, N 45.06476948, S 45.03130000
Software
No software entries listed in this EML file.
Keywords
- LTER controlled vocabulary: disturbance (theme), inorganic nutrients (theme), soil (theme), forests (theme), canopy gaps (theme)
- Andrews Experimental Forest site thesaurus: Long-Term Ecological Research (LTER) (theme)
- LTER core research areas: disturbance (theme), inorganic nutrients (theme)
Taxonomic Hierarchy
No taxonomic hierarchy listed in this EML file.
Data Entities
| # | Entity | Metadata | Data |
|---|---|---|---|
| 1 |
SP01701
SP01701 The influence of tree-fall gaps on soil characteristics in gaps of varying sizes: |
METADATA | DATA |
Metadata
SP01701 - SP01701
Object name: SP01701.csv
Records: 510
Attributes: 15
File size: 25875 byte
Checksum (MD5): e1b41645cf6bfe9d25658afb167bd73f
Format: headers=1, recordDelimiter=\r\n, fieldDelimiter=,, quoteCharacter=", orientation=column
Constraints (1)
-
notNullConstraint: NOTNULL SP01701.GAPNUMBR, SP01701.GAPSIZE, SP01701.IN_OUT, SP01701.LOCATION, SP01701.N_S, SP01701.ZONE
Attributes (15)
GAPNUMBR - numeric(3,0) (ratio)
ID: SP01701.GAPNUMBR
Site designator; gap 100 was a none-cut gap control
Type system: Microsoft SQL Server 2008
Unit: number
Precision: 1.000000
Numeric domain: type=natural, min=110.0000 (exclusive=false), max=210.0000 (exclusive=false)
GAPSIZE - numeric(2,0) (ratio)
ID: SP01701.GAPSIZE
Gap diameter in meters
Type system: Microsoft SQL Server 2008
Unit: meters
Precision: 1.000000
Numeric domain: type=natural, min=10.0000 (exclusive=false), max=50.0000 (exclusive=false)
LOCATION - numeric(2,0) (ratio)
ID: SP01701.LOCATION
Sampling location along transect
Type system: Microsoft SQL Server 2008
Unit: number
Precision: 1.000000
Numeric domain: type=whole, min=1.0000 (exclusive=false), max=50.0000 (exclusive=false)
N_S - numeric(1,0) (ratio)
ID: SP01701.N_S
Sample location north or south of gap center
Type system: Microsoft SQL Server 2008
Unit: number
Precision: 1.000000
Numeric domain: type=whole, min=0.0000 (exclusive=false), max=1.0000 (exclusive=false)
ZONE - numeric(1,0) (interval)
ID: SP01701.ZONE
1=Nout; 2=Nin; 3=Sout; 4=Sin;
Type system: Microsoft SQL Server 2008
Unit: number
Precision: 1.000000
Numeric domain: type=natural, min=1.0000 (exclusive=false), max=4.0000 (exclusive=false)
IN_OUT - char(3) (nominal)
ID: SP01701.IN_OUT
OUT = out of gap, IN = in gap
Type system: Microsoft SQL Server 2008
MOIST - numeric(5,1) (ratio)
ID: SP01701.MOIST
Percent moisture
Type system: Microsoft SQL Server 2008
Unit: percent
Precision: 0.100000
Numeric domain: type=real, min=0.0000 (exclusive=false), max=100.0000 (exclusive=false)
SOILTEMP - numeric(4,1) (ratio)
ID: SP01701.SOILTEMP
Soil temperature
Type system: Microsoft SQL Server 2008
Unit: degrees Celsius
Precision: 0.100000
Numeric domain: type=real, min=5.0000 (exclusive=false), max=15.0000 (exclusive=false)
SOM - numeric(4,1) (ratio)
ID: SP01701.SOM
Soil organic matter
Type system: Microsoft SQL Server 2008
Unit: percent
Precision: 0.100000
Numeric domain: type=real, min=5.0000 (exclusive=false), max=40.0000 (exclusive=false)
LITTER - numeric(4,1) (ratio)
ID: SP01701.LITTER
Litter depth
Type system: Microsoft SQL Server 2008
Unit: centimeters
Precision: 0.100000
Numeric domain: type=real, min=0.0000 (exclusive=false), max=20.0000 (exclusive=false)
BULKDENS - numeric(4,2) (ratio)
ID: SP01701.BULKDENS
Bulk density
Type system: Microsoft SQL Server 2008
Unit: grams per square centimeter
Precision: 0.010000
Numeric domain: type=real, min=0.0000 (exclusive=false), max=1.0000 (exclusive=false)
TOTALN - numeric(5,3) (ratio)
ID: SP01701.TOTALN
Total nitrogen
Type system: Microsoft SQL Server 2008
Unit: percent
Precision: 0.001000
Numeric domain: type=real, min=1.0000 (exclusive=false), max=1.0000 (exclusive=false)
TOTALC - numeric(5,3) (ratio)
ID: SP01701.TOTALC
Total carbon
Type system: Microsoft SQL Server 2008
Unit: percent
Precision: 0.001000
Numeric domain: type=real, min=1.0000 (exclusive=false), max=20.0000 (exclusive=false)
C_NRATIO - numeric(2,0) (interval)
ID: SP01701.C_NRATIO
Total carbon/total nitrogn
Type system: Microsoft SQL Server 2008
Unit: number
Precision: 1.000000
Numeric domain: type=natural, min=15.0000 (exclusive=false), max=45.0000 (exclusive=false)
LABRESP - numeric(3,0) (ratio)
ID: SP01701.LABRESP
Laboratory respiration rates (dry weight basis, as C)
Type system: Microsoft SQL Server 2008
Unit: micrograms per gram per hour
Precision: 1.000000
Numeric domain: type=natural, min=0.0000 (exclusive=false), max=4.0000 (exclusive=false)
Units
| grams per square centimeter | g/cm2 | arealMassDensity | gramPerCentimeterSquared | kilogramPerMeterSquared | 0.0000001 | grams per square centimeter |
| meters | m | length | meter | meter | 1 | meter; SI unit of length |
| micrograms per gram per hour | ug/g*hour | massPerMassRate | microgramPerGramPerHour | kilogramPerKilogramPerSecond | 0.0036 | micrograms per gram per hour |
| centimeters | cm | length | centimeter | meter | 0.01 | centimeters; .01 meters |
| degrees Celsius | deg c | temperature | celsiusDegree | kelvin | 1 | Degrees Celsius; a common unit of temperature; constantToSI=273.18 |
| percent | % | dimensionless | number | dimensionless | 100 | percent; a number |
| number | number | dimensionless | number | dimensionless | 1 | dimensionless number, i.e., ratio, count |
Intellectual Rights
Data Use Agreement:
The re-use of scientific data has the potential to greatly increase communication, collaboration and synthesis within and among disciplines, and thus is fostered, supported and encouraged. This Data Set is released under the Creative Commons license CC BY "Attribution" (see: https://creativecommons.org/licenses/by/4.0/). Creative Commons license CC BY - Attribution is a license that allows others to distribute, remix, tweak, and build upon your work (even commercially), as long as you are credited for the original creation. This license accommodates maximum dissemination and use of licensed materials.
It is considered professional conduct and an ethical obligation to acknowledge the work of other scientists. The Data User is asked to provide attribution of the original work if this data package is shared in whole or by individual parts or used in the derivation of other products. A recommended citation is provided for each Data Set in the Andrews LTER data catalog (see: http://andlter.forestry.oregonstate.edu/data/catalog/datacatalog.aspx). A generic citation is also provided for this Data Set on the website https://portal.edirepository.org in the summary metadata page. Data Users are thus strongly encouraged to consider consultation, collaboration and/or co-authorship with the Data Set Creator.
While substantial efforts are made to ensure the accuracy of data and associated documentation, complete accuracy of data sets cannot be guaranteed and all data are made available "as is." The Data User should be aware, however, that data are updated periodically and it is the responsibility of the Data User to check for new versions of the data. The data authors and the repository where these data were obtained shall not be liable for damages resulting from any use or misinterpretation of the data.
General acknowledgement: Data were provided by the HJ Andrews Experimental Forest research program, funded by the National Science Foundation's Long-Term Ecological Research Program (DEB 2025755), US Forest Service Pacific Northwest Research Station, and Oregon State University. If data used in publication, Robert Griffiths and Shirley King will be listed as a coauthor. Whenever these data are presented in whatever form, Griffiths and King will be acknowledged.
Licensed
License: N/A
Maintenance
Maintenance update frequency: irregular
Description
- An update history is logged and maintained with each new version of every dataset.
Change History
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Version1 (2001-05-02) Original metadata creation.
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Version2 (2002-02-08) Metadata restructured and moved into SQLServer metadata database LTERMETA. Data moved into SQLServer database FSDBDATA.