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Mesoscopes for Hydropedology in the Critical Zone

Dept. of Ecosystem Science and Management The Pennsylvania State University

henrylin@psu.edu

Henry Lin

(2)

Photo Courtesy: John A. Kelley

Understanding Soils – Their Architecture & Functional Manifestations

Heterogeneity differs from randomness: the former is associated with order while the latter is linked to disorder.

Organized heterogeneity reflects underlying structure that governs the direction and efficiency of energy and matter transfer.

Evolutionary processes have been made possible because of heterogeneity of all kinds leading to the flow of energy and mass that are driven by various gradients at different scales.

(3)

Complexity

Randomness

II. Unorganized complexity  (aggregates)

I. Organized simplicity (machines)

III. Organized complexity  (systems)

Analytical treatment

Statistical treatment

Scientific treatment?

Large number systems

Small number systems

Medium number systems

Pedon Mesoscopic

Macroscopic

Microscopic

Model Scale

i i+1 i+2 i+3 i+4

i-1

i-2

i-3

i-4 Upscaling

Downscaling Processes

& Parameters

Hillslope processes Watershed

processes Regional processes

Global processes

Pore & molecular processes Mineral-organic complex processes

Aggregate processes

Horizon processes

Zoom in Zoom out

Organized complexity: too complex for analytical treatment and too organized for statistics → This is the region of so-called medium number systems where large fluctuations, irregularities, and discrepancy with any theory occur regularly

Microscope ↔ Mesoscope ↔ Telescope

(Modified from: Weinberg, 1975)

(4)

Pattern

Variability

Fast Slow

Time

Space Systems

(5)

P

Clay Coating

0.001 m

Regional control

Soil structural units

Soil-landscape units

S I

S

P I

1 m 1 m 0.1 m 1 km

P S

I

S P

I

Soil distribution pattern viewed from space

Soil architecture under microscope Tertiary

peds

Local control

Cutans Primary

peds

Secondary peds Crayfish

biotube

(Lin, 2012, Hydropedology)

(6)

Soil Architecture Preferential Flow

(Lin, 2012, Hydropedology)

(7)

Stream Gauge

Sediment Fence

Dry (D1)

Moderately Dry (D2) Wet (W1)

Moderately Wet (W2) Subsoil Moisture Clusters of the Monitoring Sites

~100 m

N

1 E

2

3

4

5 6

9 8 7 10 11

14 13

12 15

A1 22

23

24

25

26

27

29 28

30 31

36 35

34 33 32

37 38

39 40

41

44 43

42 45

47 46 48

49

50 54

53

52 51 58 57

56 55 59

60

61 67

66 65

6364 62

71 70

69 68 73 72

A2

A3A4 A5 B2

B3B4

B5

B1

Automatic soil monitoring stations

128 15 22

40 5

68 92

162 122

(8)

(m)

Depth (cm)

Weikert Berks Rushtown Ernest Blairton

0

25

50

75 100

125

150

175

Inceptisols Ultisols

Soil Map

(9)

Site 53 right (Berks)

Date

10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Volumetric water content (m3 /m3 )

0.0 0.1 0.2 0.3 0.4 0.5

Rainfall (mm/10min)

0 10 20 30 40 50

11/16/06 11/17/06

Oe-A (5 cm) A (10 cm)

BC-C (88 cm) Bw2 (40cm)

C (103 cm)

14:03 14:12 13:52

14:06 13:53

Response time

Transient saturation

14:08 16:35

14:17 14:46

(Lin and Zhou, 2008, EJSS)

(10)

Controls and Frequency of Preferential Flow Occurrence: A 175-Event Analysis

Preferential flow was common throughout the catchment, occurring during 17 to 54% of the 175 events at each of the 10 monitored sites along a hillslope. Preferential flow occurred in at least one site during 90% of the 175 events.

While the frequency of preferential flow appeared insensitive to topographic position, the controls on preferential flow initiation varied with landscape position. While the frequency of preferential flow can be determined from 1 yr of real-time monitoring, the controls on preferential flow require much longer (≥ 3 yr) monitoring to be reliably identified.

(Graham and Lin, VZJ, 2011)

(11)

(Liu and Lin, SSSAJ, 2014)

Preferential flow occurred during <1% to 70% (overall average 26%) of 323 events over 5.5 years (2006-2012) at each of 35 monitored sites, with 90% of the events generating preferential flow in at least one site.

(12)

Ridge Top Midslope Valley Floor

Seasonal profiles show strong isotopic attenuation with depth.

In winter, preferential flow occurs along soil-horizon and soil-bedrock interfaces.

In summer, preferential flow occurs vertically through macropores.

(Thomas et al., VZJ, 2013)

(13)

A) Complex slope

B) Planar slope

C) Swale cross-section

Weikert

Berks

Rushtown

Weikert

Berks

Rushtown

Weikert Berks

Weikert

C A B

(Lin, Hydropedology, 2012)

(14)

Weikert soil

Dry

Wet

Dry

Wet Bw

BC

C Rushtown soil

(Zhang et al., 2014)

Time-lapsed GPR in combination with real-time soil water monitoring have revealed flow paths in fractured shales and the impacts of soil layering on subsurface lateral flow

(15)

5, 15, 30, 45, 60 min

53 L 53 L

5, 15, 30 min

(16)
(17)

(Guo et al., WRR, in revision)

(18)

Time‐Lapsed GPR Radargram Interpretation  After Water Infiltration into Soils

Oe and A: 0‐12 cm BW : 12‐45 cm

BC: 45‐90 cm

C: 90‐135 cm

Deep lateral macropore  flow

Vertical macropore  flow

Near‐surface lateral  macropore flow and vertical finger flow

Subsurface flow network

(Guo et al., WRR, in revision)

(19)

Earth System Physiographic

Regions Watershed

Soils Soil

Landscapes Soil

Catenae Soil

Profiles Soil

Horizons Soil

Aggregates Soil

Particles Soil

Microbes

Global Model GIS

RS

RS GIS EMI

GPR GPR ERT PT

PT GPR CT TS

CT PCR

DNA SEM TEM Synchrotron

Microprobe

Geospatial Geophysics

Microscopy Spectroscopy

Spatial scale (m)

Molecular Structures

100

Catana/Soilscape Soil sequence/zone

10-2

10-6 10-4 102 104 106

Soil structural units (soil profile features)

Soil-landscape units (soil map units)

Particle/Pore/Aggregate Horizon/Pedon

Visual

(20)

Green water: Essential in combating looming global freshwater crisis

(P. Rogers, 2008)

(21)

Vadose zone

Ground water (fresh water)

Confining unit

Aquifer (saline water)

Leaching of fertilizers &

pesticides on farmlands Septic

tank

Leaking petroleum

tank Chemical

spill Landfill leaching

Water Table

Toxic waste dump

Pumping well

Shallow well

Abandoned well

Root zone

Inter- mediate

zone

Capillary fringe

(Modified from: Fetter, 1993)

..?

Sub-basin: 3D view 10 km

100 km

River basin: plan view

d.

(Modified from McClain et al., 2003)

Biogeochemical hot spots and hot moments in the landscape

(22)

While landform and vegetation can now be mapped with high resolution, we lack adequate tools and techniques for in situ, precision, continuous, and noninvasive mapping and sensing of the complex subsurface. Improved mesoscopes (i.e., devices or techniques that are between microscopes and telescopes) are needed to shed better light on the complex subsurface in the Critical Zone.

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