25
U.S. Department of the Interior U.S. Geological Survey The Role of Flow and Transport Processes in Ridge/Slough/Tree Island Pattern Dynamics Laurel Larsen, Nicholas Aumen, Christopher Bernhardt, Vic Engel, Thomas Givnish, Scot Hagerthey, Judson Harvey, Lynn Leonard, Christopher McVoy, Gregory Noe, Martha Nungesser, Kenneth Rutchey, Fred Sklar, Tiffany Troxler, John Volin, Debra Willard U.S. Department of the Interior U.S. Geological Survey

The Role of Flow and Transport Processes in Ridge/Slough

  • Upload
    others

  • View
    3

  • Download
    0

Embed Size (px)

Citation preview

U.S. Department of the InteriorU.S. Geological Survey

The Role of Flow and Transport Processes in Ridge/Slough/Tree Island Pattern Dynamics

Laurel Larsen, Nicholas Aumen, Christopher Bernhardt, Vic Engel, Thomas Givnish, Scot Hagerthey, Judson Harvey, Lynn Leonard, Christopher McVoy, Gregory Noe, Martha Nungesser, Kenneth Rutchey, Fred Sklar, Tiffany Troxler, John Volin, Debra Willard

U.S. Department of the InteriorU.S. Geological Survey

Make sure to see…Role of Flow in a Sustainable Everglades workshop, Thursday 10:30-5:40, Royal Palm VI-VIIPoster session II, Thursday 5:40-7:00, Orchid Ballroom

(Science Coordination Team 2003)

Well-preserved

Degraded

Geography and Geomorphology

Vegetation Changes in the WCAs

(Science Coordination Team 2003)

(K. Rutchey, pers. comm.)

Also see Wu et al., Ecol. Complex. 2006

WCA-1

WCA-2

WCA-3A

WCA-3B

WCA-3B

WCA-3A

Everglades N.P.

Stability of distinct ridges and sloughs indicated from the paleoecological record

(Bernhardt and Willard, in review)

Medieval Warm Period

Little Ice Age

Land

scap

e hi

stor

yLa

ndsc

ape

hist

ory

Hydro-ecological feedbacks shape the ridge and slough landscape

Additions from Givnishet al. 2008Invasion of woody plants on more aerated ridges tree islandsP enhancement on tree islands by guanoTree island expansion/elongation limited by P transport

Additions from Givnishet al. 2008Invasion of woody plants on more aerated ridges tree islandsP enhancement on tree islands by guanoTree island expansion/elongation limited by P transport

(Larsen, Harvey, and Crimaldi, Ecological Monographs 2007)

Con

cept

ual m

odel

Con

cept

ual m

odel

Peat Accretion Feedback Governs Vertical Landscape Dimension

Ridge Tree island

(Givnish et al., Global Ecol. Biogeogr., 2008) (Larsen et al., Ecol. Monogr. 2007)

Diff

eren

tial p

eat a

ccre

tion

Diff

eren

tial p

eat a

ccre

tion

Predicted differential peat accretion behavior confirmed by PeatAccrete modelPeat accretion feedback caused vertically stable ridges, but lateral spreading still occurredVertical ridge stability was more sensitive to water level than P concentration

Nutrient supply drives differences in net rate of carbon accumulation

(Ross et al., Hydrobiologia 2006)

Diff

eren

tial p

eat a

ccre

tion

Diff

eren

tial p

eat a

ccre

tion

(Wetzel et al., Plant Ecol., in press)

Particulate nutrient transport high, but role in landscape differentiation uncertain

Particulate P = 31% of water column TP. Most P associated with microbial biomass.Suspended particle sources are bacteria and periphyton 'rain', but only infrequently benthic floc.

(Noe et al., Limnol. Oceanogr. 2007)

Diff

eren

tial p

eat a

ccre

tion:

nut

rient

tran

spor

tD

iffer

entia

l pea

t acc

retio

n: n

utrie

nt tr

ansp

ort

Flow velocities typically less than 2 cm s-1

Slough velocity 30% (Harvey) to 50% (Leonard) greater than ridge velocitySpecific discharge in slough 100% greater than ridge (Harvey)

Greater flow speed in slough

(Leonard et al., Hydrobiologia 2006)

2002-2004 2002-2007

p=0.118, F(1,33) = 2.56 p < 0.0001, F(1,842) = 31.52

(Harvey et al., in review)

Sed

imen

t red

istri

butio

nS

edim

ent r

edis

tribu

tion

Role of flow pulses in controlling surface-water velocity

0

0.2

0.4

0.6

0.8

1

Mea

nw

ate r

- col

u mn

fl ow

v elo

city

(cm

s-1 )

1

2

3

4

Wa t

ersl

ope

x10

-5

Jun 2006 Aug 2006 Oct 2006 Dec 2006 Feb 2007 Apr 2007

0

20

40

60

80

Slou

g hw

a ter

dept

h(c

m)

Rain (bar=1 cm)Inflows

Water depth

0

40

80

120

160

Ma j

o rin

flow

sto

WC

A-3

A( m

3s-1

)

SloughRidgeSlope

Max water depth

(Harvey et al., in review) Sed

imen

t red

istri

butio

nS

edim

ent r

edis

tribu

tion

Velocities highly sensitive to vegetation/ landscape pattern

(Variano et al., in review; Ho et al., in review)

Determined mean flow velocities and dispersion coefficients in landscapes with different vegetation coverage and degree of degradation using SF6 tracer

Flows are in laminar to transitional regime

Flow velocities relatively insensitive to water depth but highly sensitive to vegetation cover

Flow direction aligned with ridge and slough landscape in well-preserved regions but controlled by regional forcing (i.e., water management) in degraded regions

Sed

imen

t red

istri

butio

nS

edim

ent r

edis

tribu

tion

ANCOVA: p = 0.9295, F = 0.0081

Flow dependent on vegetation coverage

(L. Leonard, pers. comm.)

Sed

imen

t red

istri

butio

nS

edim

ent r

edis

tribu

tion

Vegetative drag is higher in ridges compared with sloughs (Harvey et al., submitted) and also in degraded regions compared with well-preserved ridge and slough regions (Variano et al., submitted)Bed shear stress in sloughs is significantly lowered by presence of Eleocharis spp. (Larsen et al., in prep.)

(Variano et al., in review)

Velocity and bed shear stress affected by vegetation community

Sed

imen

t red

istri

butio

nS

edim

ent r

edis

tribu

tion

Present-day particle concentrations low, with little ridge/slough differentiation

No difference in ambient suspended sediment concentrations and physical and biogeochemical particle characteristics between ridge and slough.Greater water discharge in sloughs results in greater material loading through sloughs compared to ridges.Suspended sediment concentrations are low, dominated by fine particles (9 μm average), and generally not related to water velocity ambient flows are below sediment entrainment thresholds. Greater sediment concentrations are associated with wind, bioturbation, and hurricanes.

23 Oct12:00

24 Oct0:00

24 Oct12:00

25 Oct0:00

2

1

0

Flow

vel

ocity

(cm

s-1)

80°0'0"W

80°0'0"W

82°30'0"W

82°30'0"W

30°0

'0"N

30°0

'0"N

27°3

0'0"

N

27°3

0'0"

N

25°0

'0"N

25°0

'0"N

22°3

0'0"

N

22°3

0'0"

N

eye Wilma

(Noe et al., in review)

(Harvey et al., in review)

Sed

imen

t red

istri

butio

nS

edim

ent r

edis

tribu

tion

Benthic Annular Flume Studies

0.12 m

PaddlesOBS

Racetrack Flume Studies

Laser Doppler velocimeter

Peat/floc bed

Dowels to simulate sawgrass

Digital floc camera

LILA Flume Tracer ExperimentsNatural Floc Mobilization Experiments

Sed

imen

t red

istri

butio

nS

edim

ent r

edis

tribu

tion

Entrainment threshold of floc seldom reached in present-day Everglades

Natural flocmobilization (Larsen et al., in review)

Depth-averaged, in field (vegetated). Agreed with modeling predictions.

N/A3.2-5.3 cm s-1

Benthic annular flume (Hagerthey. pers. comm.)

Measured 5 cm above bed, unvegetated

3-5 cm s-1~2 cm s-1

Racetrack flume (Larsen et al., in review)

Depth-averaged velocity associated with threshold bed shear stress varies with water surface slope, depth, and vegetation community

0.02 Pascalsbed shear stress (~ 4 cm s-1 in racetrack flume)

0.01 Pascalsbed shear stress (~2 cm s-1 in racetrack flume)

StudyNotesSustained entrainment

Critical entrainment threshold

Sed

imen

t red

istri

butio

nS

edim

ent r

edis

tribu

tion

Restoration RecommendationsEfforts to restore flow should focus primarily on reducing vegetative biovolume in sloughs and increasing surface-water slope by instituting a pulsed-flow regime.Bed shear stresses associated with restored flows should be at least 0.01 Pascals in sloughs.Restored flows should have low P content to maintain oligotrophic conditions and prevent vegetation compositional shifts.Sawgrass monocultures will unlikely revert to a corrugated ridge and slough landscape if flows are restored, unless sloughs are manually seeded. However, restoration of flow will preserve and enhance existing landscape patterning.

Remaining Uncertainties/Future Directions

Duration of flows needed to maintain a stable, interconnected RSLRestoration timescales – related to rates of carbon and nutrient cycling (tricky!)Surface-water slopes achievable through pulsed-flow management regimeRequired balance between flow management and vegetation manipulationParticulate nutrient sources and sinks/role of fine particles

Field/lab experimentation

G. Noe

Modeling

Simulated RSL, Larsen Ph.D thesis, 2008

Large-scale field manipulations

Rietkerk et al., Am. Naturalist 2004 Photo: V. Rivera-Monroy, LSU

Loheide and Gorelick, WRR 2007

Okavango River/Delta

Riparian zone patterning

Patterned bogs

Mangrove swampsArid-zone banded vegetation patterning

Role of transport processes in maintaining vegetation heterogeneity in Everglades similar to other systems

Status of Science Coordination Team (2003) Hypotheses

McVoy; Givnish et al. Global Ecol. Biogeogr. 2008

Unlikely. Bedrock and surface topography are not correlated.

RSL patterning reproduces underlying bedrock topography

Bernhardt, Willard; Bernhardt et al., USGS OFR 2004, Willard et al., Rev. Paleobot. Palynol. 2001

Unlikely due to wet origin of landscape, its stability over millennia, and the pervasive occurrence of RSL patterning throughout Everglades

Fire may have created initial patterning

Bernhardt, Willard; Bernhardt et al., USGS OFR 2004, Willard et al., Rev. Paleobot. Palynol. 2001

Unlikely. The RSL was aggrading at the time of formation, and the landscape formed in a wetter environment than present

Sloughs formed by erosion, arising from “consequent drainage” on recently uplifted surface

Working groups/ source

StatusHypothesis

Hyp

othe

ses

Hyp

othe

ses

Hyp

othe

ses

Hyp

othe

ses

Status of Science Coordination Team (2003) Hypotheses

Givnish, Larsen, Noe, Saunders, Troxler, Volin; Givnish et al. Global Ecol. Biogeogr. 2008; Larsen et al. Ecol. Mon. 2007

Likely explanation of vertical features/vertical stability of landscape. Role of flow in delivering nutrients and oxygen less well understood

“Positive feedback” hypothesis: ridges and tree islands accrete peat more rapidly than sloughs and in response to nutrient and oxygen concentrations and water level

Givnish, Larsen, Saunders, Volin; SCT 2003

Cannot explain degradation that has occurred in some areas with unaltered hydroperiods. However, in some places, may contribute to degradation

Altered hydroperiods (e.g., depths, duration) alone permit colonization of sloughs by emergent vegetation or cause changes in decomposition rates that induce flattening

Engel, Hagerthey, Harvey, Larsen, Leonard, Noe, Nungesser

Likely explanation of longitudinal and lateral landscape features.

Sediment transport during high flows prevented net sedimentation in sloughs and caused ridges and tree islands to elongate

Working groups/ source

StatusHypothesis

Velocity and bed shear stress affected by vegetation community

Spike Rush, Utricularia, and Periphyton

102030405060

0 0.4 0.8 1.2 1.6

Spike Rush ONLY

102030405060

1.6

No Vegetation

102030405060

0 0.4 0.8 1.2

1.60 0.4 0.8 1.2

U = 0.25

U = 0.68

U = 0.78

cm s-1

cm s-1

cm s-1

(Leonard et al., Hydrobiologia 2006) Sed

imen

t red

istri

butio

nS

edim

ent r

edis

tribu

tion

Flow speeds in “free-flowing” sites 3-5x higher than “confined” sites

(Riscassi and Schaffranek, 2004; Harvey et al., in review) S

edim

ent r

edis

tribu

tion

Sed

imen

t red

istri

butio

n

Axis 3 ≈ classic microtopographic gradient

Axis 2 ≈ proximity to tree islands gradient

(Givnish et al., Global Ecol. Biogeogr. 2008)

NMS ordination: water depth highly significant to vegetation community composition

Diff

eren

tial p

eat a

ccre

tion

Diff

eren

tial p

eat a

ccre

tion