Case study:Comal River Restoration

From RESTORE
Jump to: navigation, search
0.00
(0 votes)


To discuss or comment on this case study, please use the discussion page.


Location: 29° 42' 44", -98° 8' 7"
Edit location
Loading map...
Left click to look around in the map, and use the wheel of your mouse to zoom in and out.


Project overview

Edit project overview
Status In progress
Project web site http://www.eahcp.org/
Themes Habitat and biodiversity
Country USA
Main contact forename Casey
Main contact surname Williams
Main contact user ID
Contact organisation BIO-WEST inc.
Contact organisation web site
Partner organisations
Parent multi-site project

Edwards Aquifer Habitat Conservation Plan

This is a parent project
encompassing the following
projects
No
Project picture

Project summary

Edit project overview to modify the project summary.


The Edwards Aquifer Recovery Implementation Plan (EARIP) process led to development of the approved Habitat Conservation Plan (HCP) for the Comal Springs and Comal River system (Comal system) in New Braunfels, Texas. In relation to the Comal system, the EARIP process and HCP identifies a variety of options to improve and increase habitat of threatened and endangered species, including the fountain darter (Etheostoma fonticola), Comal Springs salamander (Eurycea sp.), Comal Springs riffle beetle (Heterelmis comalensis), Peck’s cave amphipod (Stygobromus pecki) and the Comal Springs dryopid beetle (Stygoparnus comalensis). The aquatic vegetation restoration conducted in these two Project Areas in 2013 contributes to implementation of Phase I of the HCP. At specific locations within these Project Areas, non-native vegetation species have become predominant. Increasing native vegetation will benefit the fountain darter by increasing available habitat and improving the quality of existing habitat, potentially resulting in higher fountain darter densities in these areas. Improvement of, and increased areas of, fountain darter habitat is also beneficial to many other native aquatic species. During Phase 1 and beyond, the Aquatic Vegetation Restoration in Landa Lake and Habitat Restoration in the Old Channel are vital to provide the protection necessary to support the species of concern while uncertainty regarding habitat change, species’ response, and effects of other related HCP projects are being addressed.

Monitoring surveys and results

Edit project overview to modify the Monitoring survey and results.


Monitoring of aquatic vegetation, especially during the prolonged drought that central Texas has been experiencing, is important to understanding potential impacts to fountain darters. Bryophytes (mosses) hold high densities of fountain darters and can be abundant in select locations of the Comal system (e.g., Upper Spring Run upstream of Landa Lake and in the upper portion of Landa Lake). Bryophyte stands in Landa Lake remained relatively constant between 2011-2012 (Figure 2). Cabomba, another native plant with relatively high densities of fountain darters, has been increasing in coverage in Landa Lake, and by fall 2012 it had the highest coverage that has been observed over the course of the study (Figure 2). In contrast, the aquatic vegetation in the Old Channel exemplifies the interactions between native (Lugwigia) and non-native (Hygrophila) aquatic vegetation in the river. Over the past several years, Ludwigia has become sparse (filamentous algae is rarely present), while Hygrophila has come to dominate most of the reach (Figure 3). Hygrophila flourishes in the Old Channel, and has been crowding out native Ludwigia (which has higher fountain darter densities) over the last several years. Ludwigia declined over the course of 2012 and is near the lowest coverage observed over the past decade. Bryophytes significantly increased in coverage during 2012, a ten-fold increase to the highest coverage ever observed at the Old Channel Reach. Since high densities of fountain darters occupy bryophytes in the Comal River, this could mean increased populations of the endangered fish if bryophytes remain in the Old Channel Reach. Filamentous algae, which covered a significant portion of this reach in the past, were still absent from the reach in 2012.

Lessons learnt

This case study hasn’t got any lessons learnt, you can add some by editing the project overview.


Image gallery


DSCN0477.JPG
DSCN0325.JPG
FSCN0429.JPG
ShowHideAdditionalImage.png


Catchment and subcatchment



Site

Name
WFD water body codes
WFD (national) typology
WFD water body name
Pre-project morphology
Reference morphology
Desired post project morphology
Heavily modified water body
National/international site designation
Local/regional site designations
Protected species present
Invasive species present
Species of interest
Dominant hydrology
Dominant substrate
River corridor land use
Average bankfull channel width category
Average bankfull channel width (m)
Average bankfull channel depth category
Average bankfull channel depth (m)
Mean discharge category
Mean annual discharge (m3/s)
Average channel gradient category
Average channel gradient
Average unit stream power (W/m2)


Project background

Reach length directly affected (m)
Project started 2013
Works started
Works completed
Project completed
Total cost category
Total cost (k€)
Benefit to cost ratio
Funding sources

Cost for project phases

Phase cost category cost exact (k€) Lead organisation Contact forename Contact surname
Investigation and design
Stakeholder engagement and communication
Works and works supervision
Post-project management and maintenance
Monitoring



Reasons for river restoration

Mitigation of a pressure
Hydromorphology
Biology Fish, Invertebrates
Physico-chemical
Other reasons for the project


Measures

Structural measures
Bank/bed modifications
Floodplain / River corridor Habitat restoration, Riparian planting
Planform / Channel pattern
Other
Non-structural measures
Management interventions
Social measures (incl. engagement)
Other


Monitoring

Hydromorphological quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Biological quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Physico-chemical quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Any other monitoring, e.g. social, economic

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative


Monitoring documents



Additional documents and videos


Additional links and references

Link Description

Supplementary Information

Edit Supplementary Information