1 / 12

Robert Slesak – Oregon State University Stephen Schoenholtz – Virginia Tech

Soil C Cycling Following Timber Harvest in Response to Logging Debris Retention and Herbicide Application. Robert Slesak – Oregon State University Stephen Schoenholtz – Virginia Tech Timothy Harrington – PNW Research Station, USFS. Background. Uncertainty in response of

aran
Download Presentation

Robert Slesak – Oregon State University Stephen Schoenholtz – Virginia Tech

An Image/Link below is provided (as is) to download presentation Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author. Content is provided to you AS IS for your information and personal use only. Download presentation by click this link. While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server. During download, if you can't get a presentation, the file might be deleted by the publisher.

E N D

Presentation Transcript


  1. Soil C Cycling Following Timber Harvest in Response to Logging Debris Retention and Herbicide Application Robert Slesak – Oregon State University Stephen Schoenholtz – Virginia Tech Timothy Harrington – PNW Research Station, USFS

  2. Background • Uncertainty in response of soil microbial respiration (SMR) to harvesting(disturbance) • Net effect of management practices on soil C pools • Site Productivity - Reduced soil C (soil OM) may reduce longterm soil quality

  3. Study Objectives • Treatment effects on SMR • Importance of modified soil enviro. or C input from treatments on response • Determine ifDOC concentrations • vary with treatment • Relationships between DOC and • soil respiration (see you in • New Orleans)

  4. Experimental Approach • Experimental unit = individual tree (4m2 area centered on tree) • Logging debris at either 0, 40, 80% ocular coverage • With or without sustained herbicide application • 2 sites with contrasting soil characteristics and precipitation • Treatments applied in March 2005

  5. Measures • Monthly in situ SMR • Soil temperature (0-10 cm) • Soil water DOC with tension lysimeters (60 cm) • Lab incubations (3 annually) • - constant temp and moisture • - SMR and DOC

  6. Matlock – microbial respiration

  7. Molalla – microbial respiration

  8. Lab-field comparison for April Matlock No significant differences in lab or field No significant differences in lab Sig. main effect of herbicide (p<.05) In field Molalla Suggests effect in field at Molalla probably due to modified environment

  9. Lab-Field comparison for July Matlock Significant effect of debris (p=.05) In field No significant differences in lab No significant differences in field (herb p=.11) Significant effect of debris (p=.04) and herb (p=.03) in lab Molalla Matlock – field effects probably due to modified environment Molalla – field environment may be inhibiting treatment effect - variance may mask field effect (may be C effect from herbicide)

  10. Soil Water DOC Matlock Debris F=2.19, p=.12 Molalla Debris F=5.94, p<.01

  11. Conclusions • Control of competing vegetation and logging debris reduces microbial respiration for part of the growing season - length of time varies by site • Modified SMR due primarily modified soil environment • - temperature alone does not explain response • - soil moisture most likely plays important role • Some evidence for C input effect or modified microbial community • DOC “loss” greatest in the absence of logging debris (non-sig. Matlock) • Combined (SMR+DOC) C flux greatest for 0% debris retention • - losses may be offset by C inputs (NWC) • - losses may not be greater than reference (WC) • Total soil C at end of experiment will determine net change in pool

  12. Questions?

More Related