Channel Stability of the Neosho River Downstream from John Redmond Dam, Kansas —Kyle E

Total Page:16

File Type:pdf, Size:1020Kb

Channel Stability of the Neosho River Downstream from John Redmond Dam, Kansas —Kyle E Prepared in cooperation with the KANSAS WATER OFFICE Channel Stability of the Neosho River Downstream From John Redmond Dam, Kansas —Kyle E. Juracek The stability of the Neosho River is not sufficient to conclude that John of property, general aesthetics, and channel downstream from John Redmond Dam has caused the Neosho recreation. The knowledge provided by Redmond Dam, in southeast Kansas, River channel to change more than it this study will provide some of the was investigated using multi-date otherwise would have changed without information needed to best manage the aerial photographs and stream-gage the dam. Neosho River system. information. Bankfull channel width To determine the effect of John was used as the primary indicator Redmond Dam, a study of the Neosho Description of Study Area variable to assess pre- and post-dam River that compares the channel before, channel change. Five 6-mile river during, and after completion of the dam The focus of this study was the reaches and four stream gages were was undertaken by the USGS in coop­ middle 180-mile reach of the Neosho used in the analysis. Results indicated eration with the Kansas Water Office. River between John Redmond Dam and that the overall channel response to the The objective of this study was to the Kansas-Oklahoma State line altered streamflow regime and sediment determine whether or not the Neosho (fig. 1). Throughout this reach the load introduced by the dam has been River channel has widened in response Neosho River is characterized by a minor. Aside from some localized to the changes in flow regime and meandering, gravel-bed channel. The channel widening, there was little post- sediment load introduced by the dam. channel slope averages about 1.2 feet dam change in bankfull channel width. Pre- and post-dam channel stability was per mile. Riverbank height varies from The lack of a pronounced post-dam assessed using multi-date aerial about 15 to 30 feet. The channel bed channel response may be attributable photographs and streamgage infor­ frequently is situated on bedrock. to a substantial reduction in the mation. Alluvium in the Neosho River Valley magnitude of the post-dam annual peak Important issues related to the averages about 25 feet in thickness and flows in combination with the stability of the Neosho River channel is typified by silt with a basal layer of resistance to erosion of the bed and include protection of riparian resources, sand and gravel that averages about bank materials. Also, the channel may protection of habitat for threatened and 3 feet in thickness. The channel-bank have been overwidened by a series of endangered species (for example, the materials consist mostly of cohesive silt large floods that predated construction Neosho Madtom, Noturus placidus), and clay and are relatively resistant to of the dam. and bank stabilization as related to loss erosion compared to sand banks. Also, Introduction The construction and operation of a reservoir can have a substantial effect on the stability of the river channel downstream from the dam. Since its completion in 1964, the downstream effect of John Redmond Dam on the Neosho River in southeast Kansas (fig. 1) has been much debated. Previous studies by the U.S. Army Corps of Engineers (COE) (1972) and the U.S. Geological Survey (USGS) (Studley, 1996) have indicated the possibility of channel widening. Also, anecdotal evidence of perceived channel widening has been provided by residents living along the Neosho River as far as 165 mi downstream from the dam. The available evidence, however, John Redmond Dam on the Neosho River near Burlington, southeast Kansas. U.S. Department of the Interior USGS Fact Sheet FS–088-–99 U.S. Geological Survey April 1999 John Redmond EXPLANATION Reservoir 1 John Redmond 4 Current U.S. Geological Survey Dam streamflow-gaging station—Number 95°30' Burlington 2 is map number used in table 1 Le Roy N Iola reach 1 eo Discontinued U.S. Geological Survey sh 38° o streamflow-gaging station—Number is map number used in table 1 3 Iola Le Roy reach Humboldt reach Overflow dam Humboldt 95° Boundary of Chanute Neosho River Basin R iv er Erie Neosho Erie reach River Study KANSAS area MISSOURI 4 Ar ka Parsons n Neosho River s a Basin s KANSAS Oswego reach MISSOURI Oswego OKLAHOMA ARKANSAS River Chetopa KANSAS 37° Base from U.S. Geological Survey digital data, 1:100,000, 1995 OKLAHOMA Universal Transverse Mercator projection 0 10 20 30 MILES Zone 14 & 13 Converted to Lambert Conformal Conic projection, 0 10 20 30 KILOMETERS Index map Standard parallels 33° and 45°, central meridian -98°15' Figure 1. Location of Neosho River Basin, study area, river reaches, and streamflow-gaging stations. the channel banks are typically covered used as the primary indicator variable indicators used in the delineation of the by partial to complete mature tree cover to assess channel change after the com­ bankfull channel included breaks in which may enhance bank stability at pletion of the dam. slope, the tops of point bars, and some locations. Five 6-mile river reaches were changes in vegetation. The channel Several tributaries contribute unreg­ selected for use in this study (fig. 1) centerline was added, and all ulated flow to the Neosho River down- with the objective being to obtain a information was digitized. Mean stream from John Redmond Dam. Also spatially representative sample while bankfull channel width then was noteworthy are 12 overflow dams avoiding, to the extent possible, estimated for all reaches and dates as (fig. 1) that were constructed within the localized human-caused or natural channel area divided by channel main-stem channel mostly in the 1930's conditions that might obscure channel centerline length. or 1950's. Changes in the streamflow adjustment. Human-caused conditions To compare pre- and post-dam regime attributable to the operation of include overflow dams (fig. 1), bridges, channel stability, the mean bankfull John Redmond Dam have included a and channel modifications (for channel widths for all reaches and dates decrease in the magnitudes of peak dis­ example, riprap). Natural conditions were tabulated, and pre- and post-dam charges (flows) and an increase in the include split-channel locations and hard differences were evaluated. For each magnitudes of low discharges (fig. 2) points (that is, locations where the reach, pre-dam change was computed (Studley, 1996). Post-dam suspended- channel is situated along the valley as the percentage difference in mean sediment concentrations are substant­ wall). Additional factors considered in bankfull channel width between the ially reduced immediately downstream the selection of the reaches included pre-dam and construction time periods. from the dam. proximity to John Redmond Dam and Similarly, post-dam change was the availability and usability of aerial computed for each reach as the Methods photographs. percentage difference in mean bankfull For each reach, aerial photographs channel width between the construction A stable river channel naturally were obtained for three time peri­ and post-dam time periods. The magni­ meanders across its river valley over ods—pre-dam (late 1930's), construct- tude and direction of the changes were time while maintaining approximately ion (early 1960's), and post-dam (early used to assess pre- and post-dam the same cross-sectional shape. There- 1990's). The bankfull channel area was channel stability for the individual fore, changes in channel geometry may interpreted from the aerial photographs reaches as well as the entire system. be used to infer channel instability. In for each time period and traced on a Due to various potential sources of this study, bankfull channel width was scale-stable mylar overlay. Primary error in the use of aerial photographs to measure bankfull channel widths, only a change in bankfull width of 10 per- Downstream Effects of Dams result in channel narrowing as vegetation cent or more was considered signifi­ on River Channels encroaches. An exception is the case where the channel bed is armored or cant. situated on bedrock. Unable to effect­ Information from USGS Primary changes introduced by a ively scour the resistent channel bed, the streamflow-gaging stations (fig. 1, table dam include a reduction in the river's river may instead erode laterally and thus 1) was also analyzed to assess pre- and sediment load as well as an alteration of widen its channel. Typically, channel post-dam channel stability downstream the flow regime. Typical changes in the degradation initiates near the dam flow regime include a reduction in the from the dam. A comparison of pre- following closure and eventually may magnitude of peak flows and a possible migrate a considerable distance and post-dam conditions included an increase in the magnitude of low flows. downstream (Williams and Wolman, assessment of stage-discharge, dis­ Such artificially introduced changes 1984). charge-width, discharge-area, and may trigger an adjustment by the river The type, rate, duration, and discharge-velocity relations. The as it attempts to re-establish an approxi­ downstream extent of channel degrad­ Parsons gaging station was excluded mate equilibrium between the channel ation downstream from dams are and the discharge and sediment load controlled by a number of factors, from all analyses due to back-water being transported. including discharge, sediment load, bed effects from an overflow dam located In general, rivers downstream from and bank material composition, local 2.7 miles downstream from the gage dams initially adjust by channel bed-elevation control (for example, (fig. 1, map number 4). The gaging degradation. Typically, a river will bedrock, armoring), channel geometry, stations provide site-specific inform­ scour, and thus lower, its channel bed as climate, tributary inflow, and vegetation.
Recommended publications
  • Restoration and Maintenance of the Access to the Neosho River at Jacobs Creek-John Redmond Reservoir)
    FEASIBILITY STUDY (RESTORATION AND MAINTENANCE OF THE ACCESS TO THE NEOSHO RIVER AT JACOBS CREEK-JOHN REDMOND RESERVOIR) 2008 Prepared for Kansas Water Office 901 South Kansas Topeka, KS 66612 Prepared by Watershed Institute, Inc. 1200 SW Executive Dr. Topeka, KS 66615 www.watershedinstitute.biz Cover Page Photo: Neosho River Logjam from Jacobs Landing FEASIBILITY STUDY — NEOSHO RIVER LOGJAM ASSESSMENT TABLE OF CONTENTS INTRODUCTION.......................................................................................................................................1 BACKGROUND INFORMATION...........................................................................................................2 PROJECT SETTING ...............................................................................................................................2 Neosho River Logjam..........................................................................................................................4 NEOSHO RIVER RESEARCH...............................................................................................................4 Natural and Regulated Flows/Historical Droughts ............................................................................4 High-Flow Frequency/Channel Geometry..........................................................................................5 Geomorphic Effects/Overflow Dams...................................................................................................5 Channel Stability Downstream from John Redmond Dam
    [Show full text]
  • CHECK out OTHER FISHING INFORMATION at OUR WEBSITE: Kansas Fishing: We’Ve Come a Long Way, Baby!
    Details Back Cover CHECK OUT OTHER FISHING INFORMATION AT OUR WEBSITE: www.kdwp.state.ks.us Kansas fishing: We’ve come a long way, baby! hat's right. Kansas fishing isn't what it used to be. It's much more. Oh, we still have some of the best channel, Tflathead, and blue catfishing to be found, but today Kansas anglers have great variety. If you're an old-school angler and still want to catch the whiskered fish native to our streams and rivers, you have more opportunities today than ever. Channel catfish are found in nearly every stream, river, pond, lake, and reservoir in the state. They remain one of the most popular angling species. To keep up with demand, state fish hatcheries produce mil- lions of channel cats each year. Some are stocked into lakes as fry, but more are fed and grown to catchable size, then stocked into one of many state and community lakes around the state. Our reservoirs hold amazing numbers of channel catfish, and for the most part, the reservoir cats are overlooked by anglers fishing for other species. Fisheries biologists consider channel cats an underutilized resource in most large reservoirs. For sheer excitement, the flathead catfish is still king. Monster flatheads weighing 60, 70 and even 80 pounds are caught each owned, but some reaches are leased by the department through summer. Most of the truly large flatheads come from the larger the Fishing Impoundments and Stream Habitats (F.I.S.H) rivers in the eastern half of the state, where setting limb and trot Program, while other reaches are in public ownership.
    [Show full text]
  • The 1951 Kansas - Missouri Floods
    The 1951 Kansas - Missouri Floods ... Have We Forgotten? Introduction - This report was originally written as NWS Technical Attachment 81-11 in 1981, the thirtieth anniversary of this devastating flood. The co-authors of the original report were Robert Cox, Ernest Kary, Lee Larson, Billy Olsen, and Craig Warren, all hydrologists at the Missouri Basin River Forecast Center at that time. Although most of the original report remains accurate today, Robert Cox has updated portions of the report in light of occurrences over the past twenty years. Comparisons of the 1951 flood to the events of 1993 as well as many other parenthetic remarks are examples of these revisions. The Storms of 1951 - Fifty years ago, the stage was being set for one of the greatest natural disasters ever to hit the Midwest. May, June and July of 1951 saw record rainfalls over most of Kansas and Missouri, resulting in record flooding on the Kansas, Osage, Neosho, Verdigris and Missouri Rivers. Twenty-eight lives were lost and damage totaled nearly 1 billion dollars. (Please note that monetary damages mentioned in this report are in 1951 dollars, unless otherwise stated. 1951 dollars can be equated to 2001 dollars using a factor of 6.83. The total damage would be $6.4 billion today.) More than 150 communities were devastated by the floods including two state capitals, Topeka and Jefferson City, as well as both Kansas Cities. Most of Kansas and Missouri as well as large portions of Nebraska and Oklahoma had monthly precipitation totaling 200 percent of normal in May, 300 percent in June, and 400 percent in July of 1951.
    [Show full text]
  • Species Biological Report Neosho Mucket (Lampsilis Rafinesqueana)
    Species Biological Report Neosho Mucket (Lampsilis rafinesqueana) Cover photo: Dr. Chris Barnhart (Missouri State University) Prepared by: The Neosho Mucket Recovery Team This species biological report informs the Draft Recovery Plan for the Neosho Mucket (Lampsilis rafinesqueana) (U.S. Fish and Wildlife Service 2017). The Species Biological Report is a comprehensive biological status review by the U.S. Fish and Wildlife Service (Service) for the Neosho Mucket and provides an account of species overall viability. A Recovery Implementation Strategy, which provides the expanded narrative for the recovery activities and the implementation schedule, is available at https://www.fws.gov/arkansas-es/. The Recovery Implementation Strategy and Species Biological Report are finalized separately from the Recovery Plan and will be updated on a routine basis. Executive Summary The Neosho Mucket is a freshwater mussel endemic to the Illinois, Neosho, and Verdigris River basins in Arkansas, Kansas, Missouri, and Oklahoma. It is associated with shallow riffles and runs comprising gravel substrate and moderate to swift currents, but prefers near-shore areas or areas out of the main current in Shoal Creek and Illinois River. It does not occur in reservoirs lacking riverine characteristics. The life-history traits and habitat requirements of the Neosho Mucket make it extremely susceptible to environmental change (e.g., droughts, sedimentation, chemical contaminants). Mechanisms leading to the decline of Neosho Mucket range from local (e.g., riparian clearing, chemical contaminants, etc.), to regional influences (e.g., altered flow regimes, channelization, etc.), to global climate change. The synergistic (interaction of two or more components) effects of threats are often complex in aquatic environments, making it difficult to predict changes in mussel and fish host(s) distribution, abundance, and habitat availability that may result from these effects.
    [Show full text]
  • Influence of Water Flow on Neosho Madtom
    Am. Midl. Nat. 156:305–318 Influence of Water Flow on Neosho madtom (Noturus placidus) Reproductive Behavior JANICE L. BRYAN1 Department of Fisheries and Wildlife Sciences, The School of Natural Resources, University of Missouri, Columbia 65211 MARK L. WILDHABER U.S. Geological Survey, Columbia Environmental Research Center, Columbia, Missouri 65201 AND DOUGLAS B. NOLTIE Department of Fisheries and Wildlife Sciences, The School of Natural Resources, University of Missouri, Columbia 65211 ABSTRACT.—The Neosho madtom is a small, short-lived catfish species endemic to gravel bars of the Neosho River in Kansas, Oklahoma and Missouri, U.S.A. It spawns during summer in nesting cavities excavated in gravel. Although the species has survived dam construction within the Neosho River basin, its declining numbers resulted in it being added to the federal threatened species list in 1991. To test how water flow affects the reproductive behavior of Neosho madtoms, we compared activities of male-female pairs in static versus flowing-water aquaria. Using a behavioral catalog, we recorded their behavior sequences during randomly selected 5-min nighttime periods. For males and females, Jostle and Embrace were the most performed reproductive behaviors and the Jostle-Embrace-Carousel was the most performed reproductive behavior sequence. Water flow decreased the mean frequency of occurrence, percentage of time spent and mean event duration of male Nest Building. Because Neosho madtom courtship, reproduction and parental care is a complex and extended process, disturbances such as heightened river flows during the species’ spawning season may negatively affect nest quality and reproductive success. INTRODUCTION Many environmental cues trigger spawning in temperate fish species, including food abundance, photoperiod, temperature, flooding, lunar cycles and social interaction (Bye, 1984; Munro et al., 1990).
    [Show full text]
  • Neosho River (Chanute) Water Quality Impairment: Copper
    NEOSHO BASIN TOTAL MAXIMUM DAILY LOAD Water Body/Assessment Unit: Neosho River (Chanute) Water Quality Impairment: Copper 1. INTRODUCTION AND PROBLEM IDENTIFICATION Subbasin: Upper Neosho Counties: Coffey, Anderson, Woodson, Allen, and Neosho HUC 8: 11070204 HUC 11 (HUC 14s): 050 (010, 020, 050) Drainage Area: 448 square miles (Station 560 only) Main Stem Segments: 3, 5, 6, 8, 10 starting near confluence with Crooked Creek in southeastern Coffey County and traveling downstream through Woodson and Allen Counties to northwest Neosho County at monitoring station #560 and confluence with Sutton Creek (Figure 1). Tributary Segments: Sutton Creek (35), Slack Creek (30), Charles Branch Creek (27), Onion Creek (24), Elm Creek (1050), Rock Creek (7), Spring Creek (46), Indian Creek (924), Little Indian Creek (939), Martin Creek (49), Crooked Creek (44) Designated Uses: Special Aquatic Life Support, Primary Contact Recreation; Domestic Water Supply; Food Procurement; Ground Water Recharge; Industrial Water Supply Use; Irrigation Use; Livestock Watering Use for Main Stem Segments in HUC 11070204. Impaired Use: Expected Aquatic Life Support Water Quality Standard: Acute Criterion = WER[EXP[(0.9422*(LN(hardness)))-1.700]] Hardness-dependent criteria (KAR 28-16-28e(c)(2)(F)(ii)). Aquatic Life (AL) Support formulae are: (where Water Effects Ratio (WER) is 1.0 and hardness is in mg/L). 2. CURRENT WATER QUALITY CONDITION AND DESIRED ENDPOINT Level of Support for Designated Use under 2002 303(d): Not Supporting Aquatic Life Monitoring Site: Station 560 near Chanute Period of Record Used for Monitoring and Modeling: 1985 - 2001 for Station 560. Generalized Watershed Loading Function (GWLF) modeling period for soil data is 1998 – 2002.
    [Show full text]
  • Federal Register/Vol. 68, No. 145/Tuesday, July 29, 2003/Rules And
    44466 Federal Register / Vol. 68, No. 145 / Tuesday, July 29, 2003 / Rules and Regulations areas in accordance with 44 CFR part #Depth in Dated: July 21, 2003. 60. feet above Anthony S. Lowe, ground. Interested lessees and owners of real *Elevation Mitigation Division Director, Emergency property are encouraged to review the Source of flooding and location in feet Preparedness and Response Directorate. (NGVD) proof Flood Insurance Study and Flood •Elevation [FR Doc. 03–19245 Filed 7–28–03; 8:45 am] Insurance Rate Map available at the in feet BILLING CODE 6718–04–P address cited below for each (NAVD) community. ALABAMA The base flood elevations and DEPARTMENT OF HOMELAND modified base flood elevations are made Pike Road (Town), Mont- SECURITY final in the communities listed below. gomery County (FEMA Elevations at selected locations in each Docket No. D–7558) Federal Emergency Management community are shown. Little Catoma Creek: Agency National Environmental Policy Act. Approximately 1.5 miles up- stream of the confluence of 44 CFR Part 67 This rule is categorically excluded from Little Catoma Creek Tribu- the requirements of 44 CFR part 10, tary 1 ................................. *226 Final Flood Elevation Determinations Environmental Consideration. No Approximately 2.7 miles up- environmental impact assessment has stream of the confluence of AGENCY: Federal Emergency Little Catoma Creek Tribu- been prepared. tary 1 ................................. *232 Management Agency, Emergency Regulatory Flexibility Act. The Little Catoma Creek Tributary Preparedness and Response Directorate, Mitigation Division Director of the 1: Department of Homeland Security. Approximately 4,400 feet up- Emergency Preparedness and Response ACTION: Final rule. Directorate certifies that this rule is stream of the confluence with Little Catoma Creek ..
    [Show full text]
  • GRDA), an Agency of the State of Oklahoma
    PENSACOLA PROJECT FERC No. 1494 SHORELINE MANAGEMENT PLAN As Approved by the Board of Directors on June 11, 2008 GRAND RIVER DAM AUTHORITY VINITA, OKLAHOMA PENSACOLA PROJECT FERC No. 1494 SHORELINE MANAGEMENT PLAN June 11, 2008 GRAND RIVER DAM AUTHORITY VINITA, OKLAHOMA PENSACOLA PROJECT FERC NO. 1494 SHORELINE MANAGEMENT PLAN Executive Summary The Pensacola Project (FERC No. 1494) (Project) is an existing, federally licensed hydroelectric project located in northeastern Oklahoma that is owned and operated by the Grand River Dam Authority (GRDA), an agency of the State of Oklahoma. Completed in 1940, the Project’s Pensacola Dam is the longest multi-arched dam in the world. The Pensacola Dam impounds the waters of the Grand River to form the Grand Lake O’ The Cherokees (Grand Lake). Grand Lake encompasses approximately 46,500 surface acres of water and 1,300 miles of shoreline. The Project boundary is located in close proximity to the shoreline and privately owned land is generally found mere feet from the water’s edge. Since its creation, Grand Lake has been a popular recreational and residential destination. During its history, Grand Lake has hosted the National Governor’s Conference and several nationally recognized fishing tournaments. It is the home of the nation’s oldest long distance regatta on an inland lake and the oldest yacht club in Oklahoma. Current uses of the shoreline include residential and commercial development, agriculture, and wildlife management areas. Grand Lake also has considerable value as an environmental resource. It contains significant aquatic and terrestrial habitat for a host of species. Additionally, the shoreline serves an important function in the local ecology.
    [Show full text]
  • Neosho Madtom Determined to Be Threatened
    University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln US Fish & Wildlife Publications US Fish & Wildlife Service 1990 Endangered and Threatened Wildlife and Plants; Neosho Madtom Determined To Be Threatened Follow this and additional works at: https://digitalcommons.unl.edu/usfwspubs Part of the Aquaculture and Fisheries Commons "Endangered and Threatened Wildlife and Plants; Neosho Madtom Determined To Be Threatened" (1990). US Fish & Wildlife Publications. 201. https://digitalcommons.unl.edu/usfwspubs/201 This Article is brought to you for free and open access by the US Fish & Wildlife Service at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in US Fish & Wildlife Publications by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. 21148 Federal Register / Vol. 55, No. 99 / Tuesday, May 22, 1990 I Rules and Regulations DEPARTMENT OF THE INTERIOR The Cottonwood and Spring Rivers are With the exception of mainstream part of the Neosho River drainage. Federal reservoirs, and Flint Hills Fish and Wildlife Service Specimens misidentified as furious National Wildlife Refuge at the upper Ladtom (Schilbeodes eleutherus) and end of John Redmond Reservoir, all 50 CFR Part 17 rindled madtom (Schilbeodes miurus) stream reaches in the range of the PIN 1O18-AB31 3lso were collected from the Illinois Neosho madtom are in private Ri ‘er in Sequoyah County, Oklahoma, in ownership. Endangered and Threatened Wildlife 1946 (Moore and Paden 1950). The Neosho madtom is small, with and Plants; Neosho Madtom Subsequent collections in 1948 and 1950 adults averaging less than 7.5 cm (3 Determined To Be Threatened confirmed the presence of Neosho inches) long.
    [Show full text]
  • Status Survey of the Western Fanshell and the Neosho Mucket in Oklahoma
    1990 c.3 OKLAHOMA <) PROJECT TITLE: STATUS SURVEY OF THE WESTERN FANSHELL AND THE NEOSHO MUCKET IN OKLAHOMA To determine the distribution and abundance of the freshwater mussels Cyprogenia aberti (Conrad) and Lampsilis rafinesqueana Frierson in Oklahoma. A survey to determine the status of the freshwater mussels, Cyprogenia aberti (Conrad) and Lampsilis rafinesqueana Frierson, in Oklahoma was completed during August and September, 1989. These species are also known by the common names of Western Fanshell and Neosho Mucket, respectively. The western fanshell is probably extinct in the state. It is known that the species formerly occurred in the Verdigris River in Oklahoma and as a result of this study, was determined that it had also existed in the Caney River. However, no evidence of living or fresh specimens was found in any river system in northeastern Oklahoma. The Neosho mucket has also disappeared from most of its former range within the state and presently only occurs in a segment of the Illinois River system extending from the Lake Frances dam near the Arkansas border to Lake Tenkiller. Protection for this species is recommended. This report describes efforts to determine the status of two species of freshwater mussels (Mollusca: Bivalvia: Unionidae) in Oklahoma. Both species are generally considered to be rare and have rather limited geographical distributions. Both species may meet the criteria of endangered species and thus it was considered important to gain some information as to their current status. Both species have been recorded in Oklahoma but their current abundance and distribution in the state were unknown. The western fanshell, Cyprogenia aberti (Conrad) was described in 1850 from specimens collected on the rapids of the Verdigris River, Chambers' Ford, Oklahoma (Johnson, 1980).
    [Show full text]
  • Kansas' Neosho River, Section 319 Success Story
    Section 319 NONPOINT SOURCE PROGRAM SUCCESS STORY Implementing Agricultural Best ManagementKansas Practices Reduces Bacteria in the Neosho River Runoff from cattle grazing areas contributed high levels of bacteria Waterbodies Improved to several waterbodies in Kansas’ Twin Lakes watershed, including a 20.6-mile-long segment of the Neosho River (“Neosho River near Parkerville”) and a 12.2-mile-long segment of Haun Creek, a tributary to the Neosho River. In 1998 the Kansas Department of Health and Environment (KDHE) added these waterbodies to the state’s Clean Water Act (CWA) section 303(d) list of impaired waters for violating the state’s fecal coliform (FC) bacteria water quality standard and not supporting the waterbodies’ primary contract recreation designated uses. Working with the local Kansas Watershed Restoration and Protection Strategy (KS WRAPS) Twin Lakes Project, project partners in Morris County implemented agricultural best management practices (BMPs) throughout the watershed. River monitoring data collected between 2004 and 2011 showed that the “Neosho River near Parkerville” segment and waters upstream to the river’s headwaters now meet the state’s bacteria water quality standards. As a result, in 2012 KDHE removed the two segments (“Neosho River near Parkerville” and the Haun Creek segment, totaling 32.8 miles) from the state’s list of impaired waters. Problem The headwaters of the Neosho River originate in the northwest corner of Morris County in central Kansas, which is part of the Twin Lakes watershed (Figure 1). Nestled in the Flint Hills, the Twin Lakes watershed is predominately grassland, which cov- ers 67 percent of the drainage area.
    [Show full text]
  • Kansas-Oklahoma Arkansas River Compact 1966
    Kansas-Oklahoma Arkansas River Compact 1966 K.S.A. 82a-528. Arkansas river basin compact. The legislature hereby ratifies the compact, designated as the "Arkansas river compact," between the states of Oklahoma and Kansas signed in the city of Wichita, state of Kansas, on the thirty-first day of March, 1965, by Geo. R. Benz and Frank Raab as representatives for the state of Oklahoma, Robert L. Smith and Warden L. Noe as representatives for the state of Kansas, and Trigg Twichell as representative of the United States of America, which said compact is as follows: ARKANSAS RIVER BASIN COMPACT, KANSAS-OKLAHOMA The state of Kansas and the state of Oklahoma, acting through their duly authorized compact representatives, Robert L. Smith and Warden L. Noe, for the state of Kansas, and Geo. R. Benz and Frank Raab, for the state of Oklahoma, after negotiations participated in by Trigg Twichell, appointed by the president as the representative of the United States of America, and in accordance with the consent to such negotiations granted by an act of congress of the United States of America, approved August 11, 1955 (public law 340, 84th congress, 1st session), have agreed as follows respecting the waters of the Arkansas river and its tributaries: Article I The major purposes of this compact are: A. To promote interstate comity between the states of Kansas and Oklahoma: B. To divide and apportion equitably between the states of Kansas and Oklahoma the waters of the Arkansas river basin and to promote the orderly development thereof; C. To provide an agency for administering the water apportionment agreed to herein; D.
    [Show full text]