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The Economic Value of Water and Ecosystem Preservation

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<strong>and</strong> shellfish species <strong>and</strong> estuarine life upon which such fish <strong>and</strong> shellfish are<br />

dependent (State <strong>of</strong> Texas, 2005).”<br />

In response to House Bill 2 (1985), Senate Bill 683 (1987), Senate Bill 1<br />

(1997), <strong>and</strong> other legislative directives, the Texas <strong>Water</strong> Development Board<br />

(TWDB) <strong>and</strong> the Texas Parks & Wildlife Department (TPWD) jointly maintain a<br />

data collection <strong>and</strong> analytical study program focused on determining the effects<br />

<strong>of</strong> <strong>and</strong> needs for freshwater inflows to the state's bays <strong>and</strong> estuaries. A schedule<br />

announced in 1998 provided for the study through 2006 <strong>of</strong> all <strong>of</strong> the Texas<br />

estuaries, minor bay systems, river estuaries, <strong>and</strong> coastal preserves.<br />

1.3. Introduction to the Importance <strong>of</strong> Inflows<br />

Within this context, Texas Parks <strong>and</strong> Wildlife determined that 1.15 million<br />

acre-feet <strong>of</strong> fresh water is the lowest inflow target value that fulfills the biological<br />

needs <strong>of</strong> the estuary on a seasonal basis (Texas <strong>Water</strong> Development Board,<br />

2006). Nonetheless, as water dem<strong>and</strong>s continue to increase over the next two<br />

decades, low flows during extended droughts may be prolonged to the point <strong>of</strong><br />

causing serious permanent ecological damage to the estuary. For example,<br />

during the drought <strong>of</strong> 1956, the inflow was as low as 275,082 acre-feet (Texas<br />

<strong>Water</strong> Development Board, 2006). Potential damages to the San Antonio Bay<br />

could in turn have significant adverse effects on local communities <strong>and</strong> economic<br />

activities, such as tourism <strong>and</strong> fishing that are supported by these ecosystems.<br />

San Antonio Bay is especially vulnerable to changes in timing <strong>of</strong> flows since<br />

it lacks a direct connection to the Gulf. It may become mostly fresh following a<br />

flooding event or hyper-saline during drought conditions. From 1941 to 1987, the<br />

Bay received an average <strong>of</strong> 2.3 million acre-feet <strong>of</strong> inflow annually. <strong>The</strong> overall<br />

rates <strong>of</strong> freshwater inflows increased during this period, “which can be attributed<br />

to increased urbanization in the watershed, increased groundwater pumping <strong>and</strong><br />

return flows <strong>and</strong> increased precipitation in the latter period (Longley, 1994).”<br />

In addition to the existing information regarding freshwater inflows data<br />

ecological freshwater requirements, some information also exists concerning the<br />

economic value <strong>of</strong> bays <strong>and</strong> estuarine ecosystems along the Texas coast. A July<br />

2003 publication <strong>of</strong> the State <strong>of</strong> the Bays estimated that the Texas coastal<br />

estuaries as whole generated roughly $2 billion annually from recreational fishing<br />

alone. Commercial fisheries averaged another $266 million annually (Mckinney,<br />

2003). Travel to coastal-based destinations accounts for about 30% <strong>of</strong> travel in<br />

Texas, translating into $10 billion in economic benefits each year. Much <strong>of</strong> these<br />

benefits are dependent on healthy estuaries (Mckinney, 2003).<br />

<strong>The</strong> Texas <strong>Water</strong> Resources Institute (TWRI), in the May 2001 study,<br />

“Impacts <strong>of</strong> Recreational <strong>and</strong> Commercial Fishing <strong>and</strong> Coastal Resource-Based<br />

Tourism on Regional <strong>and</strong> State Economies”, also yielded important data<br />

regarding the economic value <strong>of</strong> Texas’ estuaries (Jones <strong>and</strong> Tanyeri-Abur,<br />

2001). <strong>The</strong>ir study area covered the six Texas bays <strong>and</strong> estuaries, including the<br />

Sabine-Neches estuary, the Trinity-San Jacinto estuary, the Lavaca-Tres<br />

Palacios estuary, the Guadalupe Estuary, the Nueces-Mission-Aransas estuary,<br />

3

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