sefs 9_flury et al
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The contrasting effect of sediment methane gas voids on diffusive fluxes of soluble and sparingly soluble substances
Sabine Flury ,Ronnie N. Glud, Katrin Premke, Daniel F.
McGinnis
flury@igb-berlin.de
SEFS 9, Geneva
2015
Gas accumulation in sediments and sediment water interface
A common phenomenon
Methane O2 (photosynthetic biofilms)
http://myweb.fsu.edu/mhuettel/Projects/ONR_Gas.html
http://inhabitat.com/wp-content/blogs.dir/1/files/2013/01/green-algae-537x358.jpeg
marine freshwater
Gas tube bubbles
(Anderson and Martinez) 2015)
Gas distribution in sediments
(Cheng et al 2014) (Cheng et al 2014)
CH4 gas distribution in a lake
Gas profiles in marine sedimentsDeep gas: CH4 Surface gas: O2
Potential free gas accumulation from 0 cm to deep layers!
Enhanced pore water exchange due to ebullition
True at high bubble rates (e.g. seep sites) and in permeable sediments
http://inhabitat.com/wp-content/blogs.dir/1/files/2013/01/green-algae-537x358.jpeg
Pore water mixing
Pore water exchange
Photo – A. Maeck
In permeable and semi-permeable sediments:
Pore water flux: 3-21 x increase at high bubble rates
With 60-70 L m-2 d-1
(e.g. at seep sites)
(Cheng et al 2014)
How strong is the pore water exchange with bubble rates generally found in Lakes and
reservoirs?
E.g. Bubble rates in Lake Wohlen and Saar: 7-17 L m-2 d-1 (DelSontro et al 2010, Maeck et al 2013)
Experimental Set-UpSediment:- Muddy (Lake Müggel, Germany)- Sandy mud (Odense River, Denmark)
Tracer: - Br- (added as KBr) - Rhodamine WT
Gas production: - stimulated with Yeast Extract
Incubation Temperature:- 27 oC, dark- 20 oC, dark
Water mixing:- Eheim Aquarium pump (5L min-1)inactive sed.
live or .
Results
Tracer fluxes and Dapp reduced by 24% ! ̴
(Flury et al – in revision ES&T)
Rhodamine Bromide
Flux calculation in sediment: Fick’s first law
(Flury et al – in revision ES&T)
D in water: 10-9 m2 s-1
𝐽 i=𝐷i ∙∂𝐶i
∂ 𝑧Ji = fluxCi = concentration of diss. sp.Z = depthDi = Diffusivity of species i
In sediments:
Di = function of Tortuosity θ
Molecular diffusion:
Effect of gas voids on pore water and gas flow
(Flury et al – in revision ES&T)
D in water: 10-9 m2 s-1 D in gas: 10-5 m2 s-1
Effect of gas voids on pore water and gas diffusivities in
SOIL
𝐷us=𝐷w ∙𝛼73
𝜑2
Millington and Quirk model for water unsaturated porous media (Millington & Quirk 1961)
Dus = Diffusivity in unsaturated porous mediaDw = Diffusivity in free water or gas= volumetric water or gas content = total porosity
0.0 0.2 0.4 0.6 0.8 1.00.0
0.2
0.4
0.6
0.8
1.0
RWT sq
Br r
Br sq
RWT sq
Br r
Br sq
Dus
,s:D
s,s
Water content (vol water/vol sediment)
0.0 0.2 0.4 0.6 0.8 1.0Gas content (vol gas/vol sediment)
For soluble species:
- If gas cont ↑ then D ↓
- If water cont ↑ then D ↑
SandMud
Effect of gas voids on pore water diffusivities in SEDIMENT
(Flury et al – in revision ES&T)
Stan
dard
ized
Diffu
sivity
(-)
𝐷us=𝐷w ∙𝛼73
𝜑2
Diffu
sivity
of g
as (m
2 s-1
)Effect of gas voids on gas diffusivities in SEDIMENT
Small amounts of gas can increase Dgas substantially!
(Flury et al – in revision ES&T)
𝐷us=𝐷w ∙𝛼73
𝜑2
Implications of gas voids on:Pore water and gas fluxes - overestimation of pore water fluxes
- large underestimation of gas fluxes
Ecosystem functioning: - ↓ transport of diss. nutrients (↓internal nutrient)
- ↑ transport of e.g. CH4 to oxidizing zones - ↑ transport of O2 into sediment
http://myweb.fsu.edu/mhuettel/Projects/ONR_Gas.html
http://inhabitat.com/wp-content/blogs.dir/1/files/2013/01/green-algae-537x358.jpeg
Gas tube bubbles
marine freshwater
Thank you! Claudia Theel (IGB)
Workshop SDU
Anni Glud (SDU)
Morten Larsen (SDU)Jael Brüning (IGB)
Amanda Cheng (IGB)
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