paul montagna university of texas at austin marine science institute port aransas texas n.
Download
Skip this Video
Loading SlideShow in 5 Seconds..
Ecosystem Context of Environmental Flows PowerPoint Presentation
Download Presentation
Ecosystem Context of Environmental Flows

Loading in 2 Seconds...

play fullscreen
1 / 34

Ecosystem Context of Environmental Flows - PowerPoint PPT Presentation


  • 108 Views
  • Uploaded on

Paul Montagna University of Texas at Austin Marine Science Institute Port Aransas, Texas. Ecosystem Context of Environmental Flows. Freshwater Flows to Bays and Estuaries: Biological Definitions and Responses. Outline. Define key scientific terms What is the scientific basis

loader
I am the owner, or an agent authorized to act on behalf of the owner, of the copyrighted work described.
capcha
Download Presentation

Ecosystem Context of Environmental Flows


An Image/Link below is provided (as is) to download presentation

Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author.While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server.


- - - - - - - - - - - - - - - - - - - - - - - - - - E N D - - - - - - - - - - - - - - - - - - - - - - - - - -
    Presentation Transcript
    1. Paul Montagna University of Texas at Austin Marine Science Institute Port Aransas, Texas Ecosystem Context of Environmental Flows Freshwater Flows to Bays and Estuaries: Biological Definitions and Responses

    2. Outline • Define key scientific terms • What is the scientific basis • What science has been done

    3. Are flows to estuaries water run to waste? • No! It’s the law • 1985, HB 2 requires: “maintain a sound ecological environment” in Texas bays and estuaries. • 2001 HB 1629: “maintain the ecological health and productivity of the Matagorda Bay system.” • 2003, SB 1639 requires: “provide for the freshwater inflows necessary to maintain the viability of the state's bay and estuary systems.” • It’s not a “green issue,” it’s a water development issue • How can we provide water and still protect coastal resources?

    4. So, are there scientific definitions of these terms? • Sound ecological environment • Ecological health • Viability of the bay and estuary systems • Productivity of a bay system

    5. So, are “soundness,” “health,” and “viability” really fluffy words? • NO! • Ecological Health has been defined by scientists • The term is used EPA in specific contexts • Soundness and viability are clearly the same thing as health

    6. Ecological health • Ecological health is assessed by determining if indicators of ecological conditions are in an acceptable range. • Indicators establish an acceptable range of responses across broad spatial and temporal scales. • Condition is the status of ecological function, integrity, and sustainability. • Function is acceptable when the ecosystem provides important ecological processes. • Integrity is acceptable when biological diversity, species composition, structural redundancy, and functional processes are comparable to that of natural habitats in the same region. • Sustainability is acceptable when an ecosystem maintains a desired state of ecological integrity over time.

    7. What is biodiversity? Biological diversity

    8. What is biodiversity? Biological diversity Biological diversity

    9. What is biodiversity? Biological diversity Biological diversity Biodiversity

    10. What is biodiversity? Biological diversity Biological diversity Biodiversity

    11. Ecological indicators that work • Function • Ecological processes • Production, trophic links, reproduction • Integrity • Community structure and biodiversity • Benthos, nekton, plankton • Sustainability • Ecosystem services • Habitats, Habitats, Habitats

    12. What is production? • Mass per unit area (volume) per unit time • Energy transformation • Follow the Sun • Primary production by plants • Phytoplankton, seagrass, macroalgae, marsh • Secondary production by animals • Microbes, benthos, plankton, nekton

    13. Good (and not so good) indicators of production • Biomass or standing stock change over time • Good, but not perfect • Mass per unit area (volume), so missing time • Harvest • Not so good, • Effected mainly by regulation and economic conditions

    14. Measuring condition • Understanding variability in space and time • Long-term studies over regional scales • Distinguishing between natural and anthropogenic effects • Comparison among systems with varying human influence

    15. Applying indicators of ecological condition • Long-term studies of water quality and benthos over entire coastal bend • There is a link between inflow, nutrients, and primary production, but it is ephemeral • Benthos are fixed in place and sample that ephemeral water column • Benthos are the memory of the ecosystem

    16. Questions guiding research • Can a direct link between flow and ecosystem services be made? • Can a direct link between nutrient loading and secondary production be made? • Can restoring flow restore an ecosystem?

    17. Climatic Gradient • Climatic and soil gradient from northeast to southwest. • Concordant rain gradient. • Southwestern estuaries are neutral, barely maintaining salinities below seawater. • Extreme year-to-year variability. • Water allocation is a problem where where it is scarce.

    18. Long-term studies focused on SW, lagoonal estuaries of the Texas Coastal Bend Inflow balance 2 positive 2 neutral 2 negative LC GE MA NC LM BB Coastal BendL-T Studies

    19. Salinity Patterns

    20. Benthic Change Over Time

    21. Benthic Change Over Time Period Modeled

    22. Sun Day Fresh Water Light Length Inflows Outside Bay System Water Column Producer Water Bottom Nutrients Temperature Salinity Salinity Depth Fish Light Limitation Suspension Current (primary production) Speed Biomass Bottom Sediment C% Growth Predation Suspension-feeders Biomass Detritus Predation Growth (POC level ) Deposit-feeders Bioenergetic Productivity Model

    23. Trophic response to inflow • Bays with high inflow have high suspension feeder production • Bays with low inflow have low deposit feeder production

    24. Relationship Between Benthic Growth Rate and Nitrogen Loads

    25. Conclusions about flow indicators • Texas coast a great “natural experiment” • Nitrogen loading related to inflow • Residence times control community structure more than secondary production • Nitrogen loading adjusted for residence times related to benthic secondary production

    26. Nueces River Basin ~1 million acre-ft storage capacity in 2 reservoirs Atascosa River Frio River Choke Canyon Dam (1982) Wesley Seale Dam (1958) Nueces River Nueces Delta/Marsh

    27. Nueces Estuary Issues • Second dam built 1982. • 151,000 acre-ft/y required. • No releases due to drought and impoundment. • Salinity increased 3 fold.

    28. Nueces Delta/Marsh effects • Nueces Marsh inflow reduced by dam building to near zero • Inflow events reduced from 3/y to 1/3 years La Fruta Dam Wesley Seale Dam Choke Canyon Dam

    29. Past salinities were low Rangia cuneata middens found in Rincon Bayou. Rangia requires 5 - 10 ppt to reproduce.

    30. Nueces Estuary, Texas USA-Restoration Efforts • Nueces River bank lowered to increase flooding of Rincon Bayou and marsh. • Salinities reduced from 150 ppt to 25 ppt, productivity and diversity increased. • City received inflow credit for marsh restoration (Adaptive Management). Channel

    31. A little water goes a long way in Rincon Bayou • Just 100 ac-ft yields maximum productivity. • When salinity is lowered, abundance, biomass, and diversity increases • Optimal salinity around 20 ppt

    32. Early Post Diversion (1998/99) Late Post Diversion (2003) Allison diversion projectRestored flow to lower part of Nueces Delta Thank you Ken Dunton

    33. Conclusions about restored flows • The “reverse estuary” condition largely corrected. • A significant degree of estuarine function was restored to the delta. Partially Restored Salinity Gradient Delta 21-28 River Bay Gulf 0-1 15-30 30-36

    34. Overall conclusions • Can define useful terms (“bay health”) in scientific ways • Can measure meaning ecological indicators • Can related indicators to ecosystem services • Can perform ecosystem management of flows • Can perform adaptive management