Creek systems in restored coastal wetlands: morphological evolution and design implications
Creek systems in restored coastal wetlands: morphological evolution and design implications
Saltmarsh restoration such as managed realignment (MR) projects often include excavation of simplified tidal creek networks to improve drainage and marsh functioning, but their design is based on limited evidence. This paper compares the morphological evolution of creek networks in current MR projects in the UK with creek networks in natural saltmarshes, in order to provide improved guidance.
The evolution of creek networks was monitored for 2–20 years post-breach at 10 MR sites across the UK by semi-automatically extracting 12 morphological creek parameters from lidar. The rates of creek evolution in MR sites are linked to the initial tidal, morphological and sedimentological conditions using principal component analysis, then compared with power law relationships of morphological equilibrium defined from 13 mature natural saltmarshes.
MR creeks evolved into larger, more complex, better distributed systems, with a total creek length and volume statistically similar to their natural counterparts. However, the creek volume remains poorly distributed, with a mean distance between creeks ranging from 33 to 101 m versus 5–15 m for natural mature saltmarshes. MR creeks are also clustered around the breach area, leaving the marsh interior poorly drained. MR creek network morphologies remain strongly influenced by the initial creek template, as evidenced by unnaturally straight creeks inherited from former drainage ditches.
A combination of external conditions (i.e., tidal range, sediment concentration in the wider estuary) and local conditions (i.e., site elevation, topographical heterogeneity, soil compaction) controls how easily creeks can form within MR sites. This in turn determines the amount of engineering effort required to help achieve reference site conditions. The end goal of creek design is to create MR sites that closely resemble reference site conditions, however the final design is also likely to be affected by a range of practical factors (e.g. engineering/cost) unique to each site and project.
Blue carbon, Lidar, Managed realignment, Morphological equilibrium, Morphometry, Saltmarsh
Chirol, C.
4c819785-4361-4d1b-9905-27ae4e72659e
Pontee, N.
d7168f5a-6e4f-4aa1-b7f8-fdf81405a432
Gallop, S.L.
be66589c-137a-4e23-81d2-8e3b901a5307
Thompson, C.E.L.
2a304aa6-761e-4d99-b227-cedb67129bfb
Kassem, Hachem
658efa7a-a02c-4b29-9d07-5d57e95a4b51
Haigh, I.D.
945ff20a-589c-47b7-b06f-61804367eb2d
15 April 2024
Chirol, C.
4c819785-4361-4d1b-9905-27ae4e72659e
Pontee, N.
d7168f5a-6e4f-4aa1-b7f8-fdf81405a432
Gallop, S.L.
be66589c-137a-4e23-81d2-8e3b901a5307
Thompson, C.E.L.
2a304aa6-761e-4d99-b227-cedb67129bfb
Kassem, Hachem
658efa7a-a02c-4b29-9d07-5d57e95a4b51
Haigh, I.D.
945ff20a-589c-47b7-b06f-61804367eb2d
Chirol, C., Pontee, N., Gallop, S.L., Thompson, C.E.L., Kassem, Hachem and Haigh, I.D.
(2024)
Creek systems in restored coastal wetlands: morphological evolution and design implications.
Science of the Total Environment, 921, [171067].
(doi:10.1016/j.scitotenv.2024.171067).
Abstract
Saltmarsh restoration such as managed realignment (MR) projects often include excavation of simplified tidal creek networks to improve drainage and marsh functioning, but their design is based on limited evidence. This paper compares the morphological evolution of creek networks in current MR projects in the UK with creek networks in natural saltmarshes, in order to provide improved guidance.
The evolution of creek networks was monitored for 2–20 years post-breach at 10 MR sites across the UK by semi-automatically extracting 12 morphological creek parameters from lidar. The rates of creek evolution in MR sites are linked to the initial tidal, morphological and sedimentological conditions using principal component analysis, then compared with power law relationships of morphological equilibrium defined from 13 mature natural saltmarshes.
MR creeks evolved into larger, more complex, better distributed systems, with a total creek length and volume statistically similar to their natural counterparts. However, the creek volume remains poorly distributed, with a mean distance between creeks ranging from 33 to 101 m versus 5–15 m for natural mature saltmarshes. MR creeks are also clustered around the breach area, leaving the marsh interior poorly drained. MR creek network morphologies remain strongly influenced by the initial creek template, as evidenced by unnaturally straight creeks inherited from former drainage ditches.
A combination of external conditions (i.e., tidal range, sediment concentration in the wider estuary) and local conditions (i.e., site elevation, topographical heterogeneity, soil compaction) controls how easily creeks can form within MR sites. This in turn determines the amount of engineering effort required to help achieve reference site conditions. The end goal of creek design is to create MR sites that closely resemble reference site conditions, however the final design is also likely to be affected by a range of practical factors (e.g. engineering/cost) unique to each site and project.
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More information
Accepted/In Press date: 16 February 2024
e-pub ahead of print date: 18 February 2024
Published date: 15 April 2024
Additional Information:
Funding information:
Funding for this project came from the NERC SPITFIRE DTP and CH2M (now Jacobs). The authors declare no conflict of interest.
Publisher Copyright:
© 2024 The Authors
Keywords:
Blue carbon, Lidar, Managed realignment, Morphological equilibrium, Morphometry, Saltmarsh
Identifiers
Local EPrints ID: 487514
URI: http://eprints.soton.ac.uk/id/eprint/487514
ISSN: 0048-9697
PURE UUID: b1acb064-917d-4425-8364-62ec6dcdb0a5
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Date deposited: 22 Feb 2024 17:37
Last modified: 01 Jun 2024 01:45
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Author:
C. Chirol
Author:
N. Pontee
Author:
S.L. Gallop
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