Knowledge (XXG)

Tailwater

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species of fish from 19 unique families were present in the system. Following dam construction, only 18 species from 8 families were collected, with two families accounting for over 90% of the fish found. 30 years after the installment of the impoundment, 28 species of fish were sampled from 8 families, however 98% of the fish were either
46:. Generally measured and reported as the average water depth downstream of a hydraulic structure, tailwater can vary based on the outlet from the structure as well as downstream influences that may restrict or advance the usual flow of water from the structure. The creation of a tailwater will have significant impacts on both the 174:. Fishing in tailwaters can be very productive due to consistent water temperature and flow rates found below an impoundment. Nutrients from the lake upstream are released into the tailwater, creating a productive environment in which target fish species, usually trout, can thrive. An example of this phenomenon is the fishery at 107:
that can reduce richness, but immediately following dam completion, many native fish species can still be found. The long-term impacts on native fish communities, especially in historically warmwater systems, are especially dramatic. Before the completion of the Beaver Dam on the Ozark River, 62
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Tailwaters are also subject to changes in traditional flow rate. Some impoundments discharge a consistent amount of water which can disrupt seasonal fluctuations and extreme flow events. On the other hand, hydropeaking, the cyclical increase in discharge below a hydroelectric dam to meet power
70:. The near-shore zones of tailwaters that are submerged during hydropeaking but dry during consistent flows are far less productive areas of the waterway. Most algal species are not adapted to handle this exposure to air for extended periods of time resulting in a loss of 85:
communities assemblages largely depend on algal composition of the waterway. With the conditions created by hydropeaking in tailwaters, much of the macroinvertebrate diversity is lost resulting in a few dominant taxa. For example, the
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results in an altered aquatic ecosystem that is far from the community makeup seen before the impoundment was in place. Substrate composition in tailwaters can also impact native fish survival. Some species, such as
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The construction of a dam will often change the makeup of the body of water immediately upstream and downstream of the structure. In many cases, the water that comes out of the dam originates from the bottom of the
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account for over 95% of the total abundance in the system. Nearly half of these species are specialists who spend their entire lives underwater and do not provide energy to the surrounding terrestrial environment.
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demands, can rapidly increase tailwater flow rates. The dramatic changes in river flow can scour the river bottom, change river velocity and depth, and reduce biotic richness in the waterway.
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A fisherman at Lee's Ferry on the Colorado River. Here the angler is attempting to catch trout in a place that would be unsuitable for the cold-water fish without the dam upstream.
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experiences dramatic flow changes due to the abundance of hydroelectric dams on the river. Below the major dams, between three and seven macroinvertebrate
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is relatively cold compared to the natural temperature of waterway due to the stratification of water that occurs in reservoirs. The resulting
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Abernethy, Erin F.; Muehlbauer, Jeffrey D.; Kennedy, Theodore A.; Tonkin, Jonathan D.; Van Driesche, Richard; Lytle, David A. (June 2021).
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areas. Increased flows can also flatten nesting sites or scour eggs from the nest making spawning in a tailwater system more difficult.
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of the waterway. Consistent flows, higher temperatures, and clear water found in tailwaters create an ideal habitat for filamentous
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Native fish species are particularly endangered by tailwaters. The construction of the tailwater itself is a severe
1353: 1323: 1161: 82: 358:<0110:faciao>2.0.co;2 "Fish Assemblage Changes in an Ozark River after Impoundment: A Long-Term Perspective" 1802: 1797: 1680: 1308: 1283: 1151: 1020: 373: 1494: 1298: 1263: 1202: 948: 902: 892: 656: 478: 1774: 1303: 995: 202: 309:"Hydropeaking intensity and dam proximity limit aquatic invertebrate diversity in the Colorado River Basin" 1393: 1242: 1123: 1078: 436: 1852: 1376: 1363: 1268: 1217: 1118: 1050: 933: 143: 104: 19: 1619: 1484: 1386: 1358: 1338: 1328: 1318: 1278: 1273: 1098: 1083: 1040: 116:
species, both of which were essentially absent prior to the creation of the tailwater. This lack of
1847: 1504: 1293: 1232: 1222: 1207: 1045: 917: 786: 646: 231:"Algal Ecology in Tailwater Stream Communities: The Colorado River Below Glen Canyon Dam, Arizona" 1813: 1700: 1657: 1642: 1584: 1556: 938: 897: 631: 581: 338: 250: 71: 463:"Review of Ecological Effects of Rapidly Varying Flows Downstream from Hydroelectric Facilities" 1637: 1541: 1489: 1469: 1197: 683: 606: 482: 418: 395:
Peoples, Brandon K.; McManamay, Ryan A.; Orth, Donald J.; Frimpong, Emmanuel A. (2013-07-02).
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Blinn, Dean W.; Shannon, Joseph P.; Benenati, Peggy L.; Wilson, Kevin P. (October 1998).
1784: 1753: 1728: 1718: 1710: 1589: 1551: 1514: 1247: 1227: 907: 841: 708: 641: 636: 586: 561: 397:"Nesting habitat use by river chubs in a hydrologically variable Appalachian tailwater" 179: 175: 87: 246: 30:
refers to waters located immediately downstream from a hydraulic structure, such as a
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and an increase in organic matter that gets washed away when flow increases.
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The environmental conditions in a tailwater influence the entire
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Waters located immediately downstream from a hydraulic structure
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10.1577/1548-8659(2003)132<0110:faciao>2.0.co;2
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Valentin, S.; Wasson, J. G.; Philippe, M. (August 1995).
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can have devastating impacts on native fish assemblages.
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10.1577/1548-8659(1985)5<330:ROEEOR>2.0.CO;2
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The Colorado River tailwater below Glen Canyon Dam.
467:North American Journal of Fisheries Management 362:Transactions of the American Fisheries Society 142:created by the impoundment. The resulting dam 1428: 535: 8: 1575:List of harvested aquatic animals by weight 1500:Illegal, unreported and unregulated fishing 592:List of harvested aquatic animals by weight 274:Regulated Rivers: Research & Management 1435: 1421: 1413: 983: 966: 569: 556: 542: 528: 520: 412: 324: 194: 170:Tailwater can also refer to a type of 7: 224: 222: 14: 1016:Geothermal energy and aquaculture 875:Worshipful Company of Fishmongers 247:10.1046/j.1529-8817.1998.340734.x 1820: 1819: 1807: 1523: 655: 1808: 1289:Federated States of Micronesia 1: 54:conditions of the waterway. 1475:Fish diseases and parasites 1089:Fish diseases and parasites 461:Cushman, Robert M. (1985). 1869: 1162:Microalgal bacterial flocs 401:Ecology of Freshwater Fish 1793: 1681:Gathering seafood by hand 1521: 982: 965: 653: 568: 555: 105:environmental disturbance 78:Macroinvertebrate impacts 1495:Individual fishing quota 1026:Integrated multi-trophic 996:Aquaculture engineering 550:Fishing industry topics 437:"Cold water pollution" 286:10.1002/rrr.3450100207 158: 24: 934:World fish production 501:"Tailwater Fisheries" 156: 22: 1485:Fisheries management 235:Journal of Phycology 72:primary productivity 1643:Fishing tournaments 1505:Sustainable fishery 787:Fish protein powder 99:Native Fish impacts 1585:Commercial fishing 1557:History of fishing 939:Fishing by country 582:Commercial fishing 441:www.dpi.nsw.gov.au 207:hancockcoingov.org 159: 25: 1835: 1834: 1638:Catch and release 1542:Artisanal fishing 1490:Fisheries science 1470:Diversity of fish 1410: 1409: 1406: 1405: 1402: 1401: 1203:Freshwater prawns 961: 960: 957: 956: 684:Fish preservation 607:Midwater trawling 414:10.1111/eff.12078 326:10.1002/ecs2.3559 166:Tailwater Fishery 148:thermal pollution 83:Macroinvertebrate 1860: 1823: 1822: 1811: 1810: 1780:Fishing villages 1719:Artificial flies 1686:Handline fishing 1633:Big-game fishing 1527: 1437: 1430: 1423: 1414: 1334:Papua New Guinea 1314:Marshall Islands 984: 976:farmed fisheries 967: 855:Shrimp marketing 777:Fish hydrolysate 659: 574:Fishing industry 570: 557: 544: 537: 530: 521: 515: 514: 512: 511: 505:The Living River 497: 491: 490: 458: 452: 451: 449: 448: 433: 427: 426: 416: 392: 386: 385: 353: 347: 346: 328: 304: 298: 297: 280:(2–4): 105–119. 265: 259: 258: 226: 217: 216: 214: 213: 203:"Drainage Terms" 199: 118:species evenness 1868: 1867: 1863: 1862: 1861: 1859: 1858: 1857: 1838: 1837: 1836: 1831: 1789: 1785:Marine habitats 1758: 1729:Bite indicators 1705: 1652: 1614: 1561: 1528: 1519: 1451: 1441: 1411: 1398: 1344:Solomon Islands 1252: 1181: 1167:Photobioreactor 1138: 1060: 978: 953: 922: 879: 850:Live fish trade 836: 728: 666:Fish processing 660: 651: 642:Fishing vessels 612:Bottom trawling 564: 551: 548: 518: 509: 507: 499: 498: 494: 473:(3A): 330–339. 460: 459: 455: 446: 444: 435: 434: 430: 394: 393: 389: 355: 354: 350: 306: 305: 301: 267: 266: 262: 228: 227: 220: 211: 209: 201: 200: 196: 192: 168: 135: 133:Abiotic Impacts 101: 80: 60: 17: 12: 11: 5: 1866: 1864: 1856: 1855: 1850: 1840: 1839: 1833: 1832: 1830: 1829: 1817: 1805: 1800: 1794: 1791: 1790: 1788: 1787: 1782: 1777: 1772: 1766: 1764: 1760: 1759: 1757: 1756: 1751: 1746: 1741: 1736: 1731: 1726: 1721: 1715: 1713: 1707: 1706: 1704: 1703: 1698: 1693: 1688: 1683: 1678: 1673: 1668: 1662: 1660: 1654: 1653: 1651: 1650: 1645: 1640: 1635: 1630: 1624: 1622: 1616: 1615: 1613: 1612: 1607: 1602: 1597: 1592: 1587: 1582: 1577: 1571: 1569: 1563: 1562: 1560: 1559: 1554: 1552:Fishing vessel 1549: 1544: 1538: 1536: 1530: 1529: 1522: 1520: 1518: 1517: 1515:Wild fisheries 1512: 1507: 1502: 1497: 1492: 1487: 1482: 1477: 1472: 1467: 1461: 1459: 1453: 1452: 1442: 1440: 1439: 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Index


dam
spillway
bridge
culvert
abiotic
biotic
food web
green algae
primary productivity
Macroinvertebrate
Colorado River
taxa
environmental disturbance
sculpin
trout
species evenness
river chubs
spawning
reservoir
discharge
thermal pollution

fishery
Lee's Ferry
Colorado River
Arizona
"Drainage Terms"

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