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SP017: Influence of tree-fall gaps on soil characteristics in gaps of varying sizes in the Andrews Experimental Forest, 1995

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Status: irregular
Period: 1995-01-07 to 1995-01-08
Version: 6
Published: 2011-09-14
EDI Package ID: knb-lter-and.3115.6
Source XML: SP017_6.xml

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
  • Sherri L. Johnson - Principal Investigator
    US Forest Service ;Pacific NW Research Station ;3200 SW Jefferson Way, Corvallis, OR, 97331, USA
    Phone: 541-758-7771
    Email: sherri.johnson2@usda.gov, sherri.johnson@oregonstate.edu
  • Julia A. Jones - Principal Investigator
    Oregon State University;Department of Geosciences; Wilkinson Hall 104, Corvallis, OR, 97331-5506, USA
    Phone: (541) 737-1224
    Email: Julia.Jones@oregonstate.edu, geojulia@comcast.net
    ORCID: http://orcid.org/0000-0001-9429-8925
  • Matthew G Betts - Principal Investigator
    Department of Forest Ecosystems and Society; 201E Richardson Hall; College of Forestry; Oregon State University, Corvallis, OR, 97331
    Phone: (541) 737-3841
    Email: matt.betts@oregonstate.edu
  • Michael P. Nelson - Principal Investigator
    Department of Forest Ecosystems and Society; 201K Richarson Hall; College of Forestry; Oregon State University, Corvallis, OR, 97331
    Phone: 541-737-9221
    Email: mpnelson@oregonstate.edu
    ORCID: http://orcid.org/0000-0001-6917-4752
  • 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
  • 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
  • Robert P. Griffiths
    Role: Principal Investigator
    Oregon State University;Dept. of Forest Science;321 Richardson Hall, Corvallis, OR, 97331-5752, USA
    Phone: (541) 737-6559
    Email: bbgriff@peak.org, griff@for.orst.edu
  • Robert P. Griffiths
    Role: Abstractor
    Oregon State University;Dept. of Forest Science;321 Richardson Hall, Corvallis, OR, 97331-5752, USA
    Phone: (541) 737-6559
    Email: bbgriff@peak.org, griff@for.orst.edu
  • Robert P. Griffiths
    Role: Creator
    Oregon State University;Dept. of Forest Science;321 Richardson Hall, Corvallis, OR, 97331-5752, USA
    Phone: (541) 737-6559
    Email: bbgriff@peak.org, griff@for.orst.edu
Contact
  • Information Manager
    Andrews Forest LTER Program, US Forest Service Pacific Northwest Research Station, 3200 SW Jefferson Way, Corvallis, OR, 97331
    Email: hjaweb@fsl.orst.edu
  • Robert P. Griffiths
    Oregon State University;Dept. of Forest Science;321 Richardson Hall, Corvallis, OR, 97331-5752, USA
    Phone: (541) 737-6559
    Email: bbgriff@peak.org, griff@for.orst.edu
Publisher
  • Andrews Forest LTER Site
    Role: Publisher
    Forest Ecosystems and Society Department in Forestry, Oregon State University, 201K Richardson Hall, Corvallis, OR, 97331-5752
    Phone: (541) 737-8480
    Email: 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
  • Andrews Experimental Forest (HJA)
    W -122.26172200, E -122.10084700, N 44.28196400, S 44.19770400
    Altitude: 1631 to 1631 meter
  • 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

  • Version1 (2001-05-02)
    Original metadata creation.
  • Version2 (2002-02-08)
    Metadata restructured and moved into SQLServer metadata database LTERMETA. Data moved into SQLServer database FSDBDATA.