doc and thmp loads from a restored wetland in the delta dwr rd1601 calfed cbda staff usgs staff...
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![Page 1: DOC and THMP loads from a restored wetland in the Delta DWR RD1601 CALFED CBDA staff USGS staff Jacob A Fleck Steven J. Deverel Roger Fujii](https://reader034.vdocuments.us/reader034/viewer/2022051819/5513fa71550346d8488b45d2/html5/thumbnails/1.jpg)
DOCDOC and THMP loads from a and THMP loads from a restored wetland in the Deltarestored wetland in the Delta
DWR RD1601 CALFED CBDA staff USGS staff
Jacob A FleckJacob A Fleck
Steven J. DeverelSteven J. Deverel
Roger FujiiRoger Fujii
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Wetland restorationWetland restoration Many thousands acres of wetland Many thousands acres of wetland
restoration restoration All native wetland types: Tidal, non-tidal, mudflatAll native wetland types: Tidal, non-tidal, mudflat BenefitsBenefits
Provide habitat for native species Provide habitat for native species Improve ecosystem function Improve ecosystem function Flood protectionFlood protection Subsidence mitigation on organic soilsSubsidence mitigation on organic soils
Engineering difficulties (deep subsidence)Engineering difficulties (deep subsidence) Island in-fillIsland in-fill Setback leveesSetback levees Impounded, flow-through wetlandsImpounded, flow-through wetlands
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USGS/DWR wetland restoration USGS/DWR wetland restoration demonstration projectdemonstration project
Initially established in 1997 Initially established in 1997 Use of wetland restoration as Use of wetland restoration as
subsidence mitigation technique on subsidence mitigation technique on deeply subsided islands deeply subsided islands
Impounded, flow-through systemImpounded, flow-through system This study established in 2000 This study established in 2000
To determine the effects that wetland To determine the effects that wetland restoration will have on DOC and THMP restoration will have on DOC and THMP loads from subsided peat islands.loads from subsided peat islands.
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Demo pond setting: Demo pond setting: Twitchell IslandTwitchell Island
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Twitchell IslandTwitchell Island
Deeply subsided Deeply subsided As much as 20 ft As much as 20 ft
Peat soils dominatePeat soils dominate >10 ft remain>10 ft remain ~35% OM~35% OM
Primarily Primarily agricultureagriculture srsr cornsrsr corn
Water upwellingWater upwelling
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Twitchell Island drainageTwitchell Island drainage
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Demonstration pondDemonstration pond ?
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Soils/drainageSoils/drainage Peat soil high in CPeat soil high in C Two layersTwo layers
Zone of drain Zone of drain influenceinfluence
Well-decomposed Well-decomposed peatpeat
High hydraulic High hydraulic conductivityconductivity
Deep peatDeep peat Unaltered peat Unaltered peat Low hydraulic Low hydraulic
conductivityconductivity
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Twitchell pumping stationTwitchell pumping station
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WQ Effects?WQ Effects?
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HCX3
OH
X
OHOOC O
HCCl2 Cl
Trihalomethanes
Haloacetic Acids
MX
Halophenols
CCXn
O=
OH
CCXn
O=
CR3
Haloketones
Haloacetonitriles
O
OH
H3C
O=C
O
OH
COOHOH
CCC
O=
OH
O
OH
CO=
OH
OH C=OCH3
CH2
DOC
-OCl-OBr
CX3CN
DBPs
Drinking water concernDrinking water concern
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Study designStudy design
Collect samples of surface and subsurface Collect samples of surface and subsurface waters for DOC and THMFP analyseswaters for DOC and THMFP analyses
Combine with water flux data to calculate Combine with water flux data to calculate loadsloads
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Monitoring planMonitoring plan Surface inflow and outflow Surface inflow and outflow
Continuously monitored for water fluxContinuously monitored for water flux Weekly sampling for DOC and THMFPWeekly sampling for DOC and THMFP
PiezometersPiezometers Sampled soil water 2x/yr for seasonal Sampled soil water 2x/yr for seasonal
extremes in 2 depths at 3 piersextremes in 2 depths at 3 piers Shallow soils (0.5-2 ft)Shallow soils (0.5-2 ft) Deep peat (8-10 ft)Deep peat (8-10 ft)
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Water flux out of the pondWater flux out of the pond
0
400
800
1200
1600
2000
10/1/2001 12/30/2001 3/30/2002 6/28/2002 9/26/2002date
wat
er f
lux
(m3/
day
)
outlet ETo seepage
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Water flux (2001-2002)Water flux (2001-2002) Siphon > 95% ET = 10% Outflow = 70% ?
Seep = 20%
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Demo pond surface water Demo pond surface water DOCDOC
0.0
1.0
2.0
3.0
4.0
5.0
6.0
7.0
8.0
Oct-01 Nov-01 Jan-02 Mar-02 May-02 Jul-02 Sep-02
DO
C (
mg
/L)
inflow outflow 1 outflow 2
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DOC concentrations in soil water DOC concentrations in soil water underlying the pondunderlying the pond
0
20
40
60
80
100
120
140
160
180
200
Jan-00 Jul-00 Jan-01 Jul-01 Jan-02 Jul-02 Jan-03 Jun-03 Dec-03 Jun-04 Dec-04
DO
C (
mg
/L)
hdp hsp jdp jsp kdp ksp
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DOC loads (2001-2002)DOC loads (2001-2002) Siphon = 940 kg/yr Outflow ~ 1260 kg/yr ?
Seep ~ 2680 kg/yr
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THMP loads (2001-2002)THMP loads (2001-2002) Siphon = 120 kg/yr Outflow ~ 160 kg/yr ?
Seep ~ 270 kg/yr
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Compare net loads to agCompare net loads to agDOC loads
0
20
40
60
80
100
120
140
160
180
200
Demo pond Ag field 1 Ag field 2
DO
C (
g/m
2-yr
)
agriculture
seepage
surface water
THMP loads
0
2
4
6
8
10
12
14
16
18
20
Demo pond Ag field 1 Ag field 2
TH
MP
s (g
/m2-
yr)
agriculture
seepage
surface water
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Temporal trendsTemporal trends
Surface water fluxes show strong Surface water fluxes show strong seasonal trendseasonal trend
Subsurface DOC concentrations are Subsurface DOC concentrations are decreasing over time in some decreasing over time in some shallow soil water (2001-2004) shallow soil water (2001-2004)
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DOC concentrations in surface DOC concentrations in surface water (2001-2002)water (2001-2002)
0
1
2
3
4
5
6
Oct
ob
er
No
vem
be
r
De
cem
be
r
Jan
ua
ry
Fe
bru
ary
Ma
rch
Ap
ril
Ma
y
Jun
e
July
Au
gu
st
Se
pte
mb
er
DO
C (
mg
/L)
outflowinflow
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Net DOC flux out of the pond Net DOC flux out of the pond (surface waters, 2001-2002)(surface waters, 2001-2002)
0.0
0.5
1.0
1.5
2.0
2.5
3.0
Octo
ber
No
vem
ber
De
cem
ber
Janu
ary
Feb
ruary
Ma
rch
April
Ma
y
June
July
Augu
st
Septe
mbe
r
OC
flu
x (
g/m
2)
DOC (g/m2-mo)
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THMFP (surface water) THMFP (surface water)
0
100
200
300
400
500
600
700
Oct
ob
er
No
vem
be
r
De
cem
be
r
Jan
ua
ry
Fe
bru
ary
Ma
rch
Ap
ril
Ma
y
Jun
e
July
Au
gu
st
Se
pte
mb
er
TH
MP
(u
g/L
)
outflow
inflow
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Net THMP flux from the pond Net THMP flux from the pond (surface waters, 2001-2002)(surface waters, 2001-2002)
0.000
0.050
0.100
0.150
0.200
0.250
0.300
0.350O
cto
be
r
No
ve
mb
er
De
ce
mb
er
Ja
nu
ary
Fe
bru
ary
Ma
rch
Ap
ril
Ma
y
Ju
ne
Ju
ly
Au
gu
st
Se
pte
mb
er
TH
M p
rec
urs
or
flu
x (
g/m
2)
THM
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Subsurface trendsSubsurface trends
0
20
40
60
80
100
120
140
160
180
200
Jan-00 Jul-00 Jan-01 Jul-01 Jan-02 Jul-02 Jan-03 Jun-03 Dec-03 Jun-04 Dec-04
DO
C (m
g/L)
hdp hsp jdp jsp kdp ksp
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Subsurface fluxes Subsurface fluxes (estimated)(estimated)
Seepage governed by hydraulic headSeepage governed by hydraulic head ~240 m3/day~240 m3/day
Concentration in shallow soils Concentration in shallow soils declined over timedeclined over time Pier H (2001) = 60 mg/L ~ 200 g/mPier H (2001) = 60 mg/L ~ 200 g/m22-yr-yr Pier H (2004) = 25 mg/L ~ 85 g/mPier H (2004) = 25 mg/L ~ 85 g/m22-yr-yr Pier K ~ 160 mg/L ~ 440 g/mPier K ~ 160 mg/L ~ 440 g/m22-yr -yr
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Temporal trend summaryTemporal trend summary
Wetland net surface fluxes are seasonalWetland net surface fluxes are seasonal Higher in summer and lower in winterHigher in summer and lower in winter Opposite trend of ag operationsOpposite trend of ag operations
Subsurface fluxesSubsurface fluxes No apparent seasonal trend (lack of data?)No apparent seasonal trend (lack of data?) Concentration (fluxes) have been decreasing Concentration (fluxes) have been decreasing
over time for soils in flow pathover time for soils in flow path
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DOC “quality”?DOC “quality”?
DOC quality differs in source of DOC and DOC quality differs in source of DOC and processing in the environmentprocessing in the environment We would expect ag, wetland soil, and We would expect ag, wetland soil, and
surface water DOC to differ in qualitysurface water DOC to differ in quality Food source vs drinking water problem?Food source vs drinking water problem?
Different carbon structures react differently Different carbon structures react differently in DBP formationin DBP formation
Some DOC structures are tasty some are notSome DOC structures are tasty some are not
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DOC “quality”DOC “quality”
5
6
7
8
9
10
11
12
13
14
15
0.02 0.04 0.06 0.08 0.1 0.12 0.14SUVA
ST
HM
FP
demo pond surface water
agricultural surface soil water
permanently flooded soil water
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ConclusionsConclusions Demo pond contributes more DOC and THMPs Demo pond contributes more DOC and THMPs
to Delta waters than nearby ag fields (>10x)to Delta waters than nearby ag fields (>10x) Most of demo pond loads derived from Most of demo pond loads derived from
seepage through the shallow soilsseepage through the shallow soils If contribution from shallow soils minimized…If contribution from shallow soils minimized…
Demo pond loads would be more comparable to ag Demo pond loads would be more comparable to ag operations (DOC ~2x, THMPs ~4x)operations (DOC ~2x, THMPs ~4x)
Timing of loads would be different from ag Timing of loads would be different from ag operations (benefits?)operations (benefits?)
Demo pond surface water DOC is more Demo pond surface water DOC is more reactive, but also more likely beneficial for reactive, but also more likely beneficial for food web (?)food web (?)
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ImplicationsImplications Design of large-scale wetland restoration Design of large-scale wetland restoration
sites need to consider shallow soil sites need to consider shallow soil contributions to drain flowcontributions to drain flow
Need to consider the effect changing the Need to consider the effect changing the DOC load timing from converted fields will DOC load timing from converted fields will have on Delta ecosystems and drinking have on Delta ecosystems and drinking water facilities?water facilities?
Need to balance potential benefits for Need to balance potential benefits for subsidence mitigation, habitat restoration subsidence mitigation, habitat restoration and food web dynamics with potential and food web dynamics with potential threats to drinking water supplythreats to drinking water supply
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Future and ongoing workFuture and ongoing work
Twitchell South pondTwitchell South pond Using lessons from demo ponds to monitor loads Using lessons from demo ponds to monitor loads
before, during, and after conversionbefore, during, and after conversion Expand studies to include other priorities (ie: MeHg)Expand studies to include other priorities (ie: MeHg)
Rice project Rice project Using water management lessons to help determine Using water management lessons to help determine
BMPs for reducing DOC loads from rice fields in BMPs for reducing DOC loads from rice fields in DeltaDelta
Compare conversion of corn fields to rice with Compare conversion of corn fields to rice with conversion to wetland conversion to wetland
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Questions?Questions?