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Soil respiration of three chronosequences in Chequamegon National Forest

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Empirical Relations with Microclimate. Type of curve fitted depends on data range ... Redrawn from Barnes et al 1980. Autotrophic and heterotrophic respiration ... – PowerPoint PPT presentation

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Title: Soil respiration of three chronosequences in Chequamegon National Forest


1
Soil respiration of three chronosequences in
Chequamegon National Forest
James M. Le Moine 24 November 2004
2
Overview
  • Introduction to soil respiration
  • Soil respiration models
  • Study objectives
  • Study site, respiration measurements
  • Statistics
  • Results
  • Summary of key findings
  • Future work

3
Soil Respiration
Respiration
Food
Energy Waste
4
Soil Respiration and the Carbon cycle
Soil 4th largest pool 2nd largest source to
atmosphere
http//earthobservatory.nasa.gov
5
Empirical Relations with Microclimate
SRR (gCO2 m-2hr-1)
Soil Moisture ()
Soil Temperature (oC)
  • Type of curve fitted depends on data range
  • SRRtSRR0e(qt)
  • Q10 change in response for 10 Cº increase in
    temperature

6
Established Trends
GPP
Ra
Flux relative to GPP
Rh
Time Since Disturbance
Redrawn from Barnes et al 1980
  • Autotrophic and heterotrophic respiration change
    with maturation.
  • Soil respiration is comprised of Rh and Ra.

7
Unanswered Questions
Does soil respiration have a trend with
maturation? Do different ecosystems have
different trends in soil respiration with
maturation? Are soil respirationtemperature
relationships consistent across maturation
classes?
8
Objectives
  • Model SRR from temperature in clearcuts and three
    age classes of hardwood, jack pines, and red
    pines
  • Compare SRR, and its temperature sensitivity
    across forest types, age classes, and age class
    within forest types.
  • Correlate SRR and its temperature sensitivity to
    common, easily obtained, vegetation and soil
    metrics
  • Compare the above correlations across forest
    types, age classes, and age classes within forest
    types

9
Study site
Chequamegon National Forest
  • Heavily managed forest
  • 34200 m of outwash sands and loamy sands
  • Growing season
  • 120 to 140 days
  • Precipitation
  • 66 to 70 cm rain and 106150cm snow

Figure adapted from Steve Mather
10
Vegetation Types and Age Classes
  • Recent Clear Cuts 1, 2, and 4 years since cut
  • Mixed hardwoods
  • 12, 14, 17,19 years 21, 22, 26
    years 71, 74, 79 years
  • Jack Pine Plantations and naturally regenerated
  • 11,11,13 years 19, 19, 21, 29 years 68, 68,
    69 years
  • Red Pine Plantations
  • 11,12,14,14 years 23, 24, 24, 31, 32 years 71,
    72, 74 years

11
Soil Respiration Measurements
  • 8 soil respiration collars
  • Soil respiration rate
  • Soil temperature (5cm)
  • Gravimetric soil moisture
  • Measurements every 2 wks
  • mid Juneearly September 02
  • late Aprillate October 03

12
Statistical Analysis
  • Shapiro-Wilk (a0.01)verification of normality
  • Nonlinear regressionSRRtSRR0e(qt)
  • Analyses of Variance (ANOVAs) on SRR0, Q10, SRR15
  • Vegetation Type and Age Class(Vegetation)
  • Vegetation Type
  • Age Class

13
Nonlinear Regression
14
Model fits
Predicted SRR (g CO2 m-2 h-1)
Predicted 0.9408Actual R2 0.6776
Actual SRR (g CO2 m-2 h-1)
Average model had n15,SRR0 0.14, Q102.91,
R20.94
15
Temperature and Moisture Correlation
Spearman-0.4930, p0.0001
SRR (g CO2 m-2 h-1)
Gravimetric soil moisture ()
Individual plot correlations ranged from -0.59 to
-0.80
16
Temperature Data Range
17
Temperature Data Range
  • No data prior to 15 May or post 23 August

18
Effects on Q10
  • Given SRRtSRR0e qt
  • Q10e10q
  • Q10 all data e 100.1224
  • 3.40
  • Q10 parsed 2.30

19
Similarity of SRR0
20
Q10 by Age within Vegetation Type
  • Nested Age not significant
  • Young and intermediate hardwoods greater than
    other groups

21
Q10 by Vegetation Type
Q10 by Age Class
a
a
a
a
  • Hardwood SRR is more temperature sensitive than
    others
  • There is no consistent age effect on Q10

22
SRR15 by Age within Vegetation Type
Vegetation type and age class
  • Nested Age not significant
  • Young and intermediate SRR15 greater than other
    groups

23
SRR15 by Vegetation Type
SRR15 by Age Class
  • Hardwood SRR15 is more temperature sensitive than
    others
  • There is no consistent age effect on SRR15

24
Summary
  • Temperature alone explains 94 of variation in
    SRR. Temperature and moisture strongly
    negatively correlated.
  • All SRR0 similar. Reflects severe temperature
    limitation.
  • Mean Q10 similar to global average of 2.4. As is
    the range of values (Raich and Schlesinger, 1992)
  • Considerable variation between replicates.
  • Statistically only need 1 model for hardwoods and
    1 model for all other ecosystems.

25
Objectives
  • Model SRR from temperature in clearcuts and three
    age classes of hardwood, jack pines, and red
    pines
  • Compare SRR, and its temperature sensitivity
    across forest types, age classes, and age class
    within forest types.
  • Correlate SRR and its temperature sensitivity to
    common, easily obtained, vegetation and soil
    metrics
  • Compare the above correlations across forest
    types, age classes, and age classes within forest
    types

26
Vegetation and Soils
  • Age (Ewel, 1987 Field Fung, 1999 Law et al
    2001 Pypker Fredeen, 2003 and others)
  • Basal Area (BA)
  • Foliage Mass (FL)
  • Canopy Cover (Cover)
  • Down Woody Debris (CWD, IWD, FWD) Mallik Hu 2001
  • Litter Depth (LD) Euskirchen 2003
  • Depth of Organic layer (OD)

27
Vegetation and Soils
28
Foliage Mass
  • HaDb
  • FL(cDd)(He)
  • Ddiameter at breast height
  • HHeight
  • FLFoliage mass
  • a, b, c, d, e species specific coefficients
  • Crow and Erdman, 1983 Perala Alban, 1994
    Ter-Mikaelian and Korzukhin, 1997 and
    Young et al. 1980

29
Linear Correlation
  • Three steps
  • Overall
  • By Vegetation Type
  • By Age Class
  • Pearson correlation for normally distributed data
  • Spearman correlation for non-normal
  • Significance 0.05
  • Marginal Significance 0.05 to 0.10

30
SRR0 Correlation
  • Negatively correlated with Q10at all levels
  • No correlation with vegetation or soil variables

31
Q10 Correlation with Vegetation
  • Overall BA, FL, Cover
  • Vegetation Type
  • Hardwood Cover
  • Jack Pine none
  • Red Pine -FWD
  • Age Class
  • Young marginal BA
  • Intermediate none
  • Mature Cover

32
Q10 Correlation with Soils
  • Overall Positive correlation with OD
  • Vegetation Type
  • Hardwood Positive with LD, OD
  • Jack Pine none
  • Red Pine none
  • Age Class
  • Young none
  • Intermediate OD
  • Mature none

33
SRR15 Correlation with Vegetation
  • Overall Age, BA, FL, Cover
  • Vegetation Type
  • Hardwood Cover, marginal CWD
  • Jack Pine none
  • Red Pine Cover, marginally BA
  • Age Class
  • Young BA, FL, Cover
  • Intermediate none
  • Mature none

34
SRR15 Correlation with Soils
  • Overall LD, OD
  • Vegetation Type
  • Hardwood OD
  • Jack Pine none
  • Red Pine none
  • Age Class
  • Young LD, OD
  • Intermediate none
  • Mature OD

35
Correlation Summary
  • SRR15 had more correlations with vegetation and
    soil variables than did Q10
  • Canopy cover has most correllates of vegetation
    variables. Depth of the organic layer is a
    better correlate than litter depth.
  • Hardwoods had more correlations than did pines
  • The young age class had more correlations than
    did inermediate or mature

36
Future work
  • SRR flux source partitioning
  • SRR as related to stand GPP and NEE
  • Improve landscape level estimates of CO2 efflux
  • SRR as related to soil CN, root abundance, root
    turnover, and differences in microbial community.

37
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