Historical Geomorphology of the Verde River
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Reevaluating Evidence for the Pre-Lllinoian Entrenchment of Northeastern Iowa River Valleys
Journal of the Iowa Academy of Science: JIAS Volume 95 Number Article 3 1988 Reevaluating Evidence for the Pre-lllinoian Entrenchment of Northeastern Iowa River Valleys Curtis M. Hudak University of Iowa Let us know how access to this document benefits ouy Copyright © Copyright 1989 by the Iowa Academy of Science, Inc. Follow this and additional works at: https://scholarworks.uni.edu/jias Part of the Anthropology Commons, Life Sciences Commons, Physical Sciences and Mathematics Commons, and the Science and Mathematics Education Commons Recommended Citation Hudak, Curtis M. (1988) "Reevaluating Evidence for the Pre-lllinoian Entrenchment of Northeastern Iowa River Valleys," Journal of the Iowa Academy of Science: JIAS, 95(4), 109-113. Available at: https://scholarworks.uni.edu/jias/vol95/iss4/3 This Research is brought to you for free and open access by the Iowa Academy of Science at UNI ScholarWorks. It has been accepted for inclusion in Journal of the Iowa Academy of Science: JIAS by an authorized editor of UNI ScholarWorks. For more information, please contact [email protected]. ]our. Iowa Acad. Sci. 95(4): 109-113, 1988 Reevaluating Evidence for the Pre-lllinoian Entrenchment of Northeastern Iowa River Valleys 1 CURTIS M. HUDAK2 Department of Geology, University of Iowa, Iowa City, Iowa 52242 Previous workers have proposed a pre-Illinoian age for the deepest bedrock entrenchment of northeastern Iowa valleys. Lines of evidence used ro support a pre-Illinoian age of entrenchment are: ( 1) deep bedrock-entrenchment interpreted ro take "long" periods of time, (2) "valleys" filled with "red-weathered drift", which was interpreted as "old", (3) differences in cross-valley profiles supposedly related to glacial advances, (4) thick beds of gravel could only be deposited by outwash streams, and (5) glacially buried (drift-filled) bedrock valleys exist outside of the Paleozoic Plateau ro the west and south. -
Status and Ecology of Mexican Spotted Owls in the Upper Gila Mountains Recovery Unit, Arizona and New Mexico
Status and Ecology of Mexican Spotted Owls in the Upper Gila Mountains Recovery Unit, Arizona and New Mexico Joseph L. Ganey James P. Ward, Jr. David W. Willey United States Forest Rocky Mountain General Technical Report Department Service Research Station RMRS-GTR-256WWW of Agriculture May 2011 Ganey, Joseph L.; Ward, James P. Jr.; Willey, David W. 2011. Status and ecology of Mexican spotted owls in the Upper Gila Mountains recovery unit, Arizona and New Mexico. Gen. Tech. Rep. RMRS-GTR-256WWW. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 94 p. Abstract This report summarizes current knowledge on the status and ecology of the Mexican spot- ted owl within the Upper Gila Mountains Recovery Unit (UGM RU). It was written at the request of U.S. Forest Service personnel involved in the Four Forests Restoration Initia- tive (4FRI), a collaborative, landscape-scale restoration effort covering approximately 2.4 million ac (1 million ha) across all or part of four National Forests (Apache-Sitgreaves, Coconino, Kaibab, and Tonto National Forests) located within the UGM RU. The UGM RU supports >50% of the known population of Mexican spotted owls, and the central location of the UGM RU within the overall range of the owl appears to facilitate gene flow throughout that range. Consequently, the UGM population is viewed as important to stability within the overall range of the owl, and management that impacts owls within the UGM RU could affect owl populations beyond that RU. Keywords: abundance, demography, habitat selection, diet composition, movements Authors Joseph L. -
June 2021 Arizona Office of Tourism Monthly State Parks Visitation Report
June 2021 Arizona Office of Tourism Monthly State Parks Visitation Report Arizona State Park Visitation June June 2021 2020 YTD State Park % Chg 2021 2020 YTD YTD % Chg Alamo Lake SP 1,237 1,924 -35.7% 48,720 46,871 3.9% Buckskin Mountain SP 11,092 9,292 19.4% 49,439 45,627 8.4% Catalina SP 6,598 2,420 172.6% 154,763 156,234 -0.9% Cattail Cove SP 10,138 14,908 -32.0% 52,221 67,256 -22.4% Colorado River SHP 167 57 193.0% 2,589 6,220 -58.4% Dead Horse Ranch SP 17,142 18,748 -8.6% 126,799 120,044 5.6% Fool Hollow Lake RA 16,380 25,104 -34.8% 55,360 63,341 -12.6% Fort Verde SHP 706 521 35.5% 4,672 2,654 76.0% Granite Mountain Hotshots MSP 1,076 1,380 -22.0% 11,778 14,874 -20.8% Homolovi SP 4,032 1,982 103.4% 22,007 11,470 91.9% Jerome SHP 4,099 1,991 105.9% 21,789 14,109 54.4% Kartchner Caverns SP 7,776 2,045 280.2% 44,020 57,663 -23.7% Lake Havasu SP 66,040 74,493 -11.3% 241,845 337,920 -28.4% Lost Dutchman SP 4,198 3,651 15.0% 122,844 132,399 -7.2% Lyman Lake SP 11,169 10,625 5.1% 30,755 38,074 -19.2% McFarland SHP 166 0 1,213 2,942 -58.8% Oracle SP 270 486 -44.4% 6,994 9,191 -23.9% Patagonia Lake SP 25,058 30,706 -18.4% 118,311 126,873 -6.7% Picacho Peak SP 1,893 1,953 -3.1% 64,084 68,800 -6.9% Red Rock SP 12,963 6,118 111.9% 56,356 33,228 69.6% Riordan Mansion SHP 777 0 2,188 2,478 -11.7% River Island SP 2,623 3,004 -12.7% 18,089 19,411 -6.8% Roper Lake SP 8,049 12,394 -35.1% 52,924 49,738 6.4% Slide Rock SP 54,922 33,491 64.0% 231,551 110,781 109.0% Tombstone Courthouse SHP 2,875 1,465 96.2% 18,261 16,394 11.4% Tonto Natural Bridge SP 8,146 7,161 13.8% 54,950 36,557 50.3% Tubac Presidio SHP 261 117 123.1% 4,240 2,923 45.1% Yuma Territorial Prison SHP 2,206 1,061 107.9% 28,672 26,505 8.2% Total All Parks 282,059 267,097 5.6% 1,647,434 1,620,577 1.7% Note: Dankworth Pond SP data is included in Roper Lake SP, Sonoita Creek SNA is included in Patagonia Lake SP and Verde River Greenway SNA is included in Dead Horse Ranch SP. -
Fossil Creek Hydrology & Travertine Geomorphology
Fossil Creek Hydrology & Travertine Geomorphology FERC Project No. 2069-003 Arizona Childs and Irving Hydropower License Prepared For: Arizona Public Service Company Phoenix, Arizona Prepared By: W.L. Bouchard & Associates, Inc. Phoenix, Arizona June 25, 1998 Fossil Creek Hydrology & Travertine Geomorphology Abstract Fossil Creek is a tributary of the Verde River in Gila and Yavapai Counties in Arizona. Stream flow is composed of a 43 cubic foot per second (cfs) base flow from Fossil Springs (a perennial source of spring flow to the creek) and runoff from precipitation which frequently occurs as destructive flash floods. These sources form 77% and 23% of the flow respectively. Fossil Springs water is supersaturated with calcium carbonate and carbon dioxide and thus tends to precipitate travertine in the upper 4 mile reach of this 14 mile stream. Travertine deposition effects stream morphology. Fossil Creek is a "flashy" stream that frequently conveys large volumes of water very quickly. Significant floods that overflow the low flow channel banks and transport significant quantities of sediment and debris Occur about every other year. These frequent flood flows tend to alter travertine deposition. Periodically, Fossil Creek is subject to very large destructive floods that significantly alter stream morphology. Arizona Public Service Company (APS) owns and operates the Childs & Irving Hydroelectric plants on Fossil Creek. The plants withdraw the 43 cfs base flow about 0.2 miles below the springs for hydropower generation. In 1992, APS proposed to the Federal Energy Regulatory Commission (FERC) to increase minimum flow releases to 10 cfs in the Irving reach and 5 cfs in the Childs reach as part of their application for relicensing. -
Appendix a Assessment Units
APPENDIX A ASSESSMENT UNITS SURFACE WATER REACH DESCRIPTION REACH/LAKE NUM WATERSHED Agua Fria River 341853.9 / 1120358.6 - 341804.8 / 15070102-023 Middle Gila 1120319.2 Agua Fria River State Route 169 - Yarber Wash 15070102-031B Middle Gila Alamo 15030204-0040A Bill Williams Alum Gulch Headwaters - 312820/1104351 15050301-561A Santa Cruz Alum Gulch 312820 / 1104351 - 312917 / 1104425 15050301-561B Santa Cruz Alum Gulch 312917 / 1104425 - Sonoita Creek 15050301-561C Santa Cruz Alvord Park Lake 15060106B-0050 Middle Gila American Gulch Headwaters - No. Gila Co. WWTP 15060203-448A Verde River American Gulch No. Gila County WWTP - East Verde River 15060203-448B Verde River Apache Lake 15060106A-0070 Salt River Aravaipa Creek Aravaipa Cyn Wilderness - San Pedro River 15050203-004C San Pedro Aravaipa Creek Stowe Gulch - end Aravaipa C 15050203-004B San Pedro Arivaca Cienega 15050304-0001 Santa Cruz Arivaca Creek Headwaters - Puertocito/Alta Wash 15050304-008 Santa Cruz Arivaca Lake 15050304-0080 Santa Cruz Arnett Creek Headwaters - Queen Creek 15050100-1818 Middle Gila Arrastra Creek Headwaters - Turkey Creek 15070102-848 Middle Gila Ashurst Lake 15020015-0090 Little Colorado Aspen Creek Headwaters - Granite Creek 15060202-769 Verde River Babbit Spring Wash Headwaters - Upper Lake Mary 15020015-210 Little Colorado Babocomari River Banning Creek - San Pedro River 15050202-004 San Pedro Bannon Creek Headwaters - Granite Creek 15060202-774 Verde River Barbershop Canyon Creek Headwaters - East Clear Creek 15020008-537 Little Colorado Bartlett Lake 15060203-0110 Verde River Bear Canyon Lake 15020008-0130 Little Colorado Bear Creek Headwaters - Turkey Creek 15070102-046 Middle Gila Bear Wallow Creek N. and S. Forks Bear Wallow - Indian Res. -
Synthesis of Upper Verde River Research and Monitoring 1993-2008
Chapter 8 A Preliminary View of Water Quality Conditions of the Upper Verde River Alvin L. Medina Introduction Stream water temperatures are of general interest because of interactive ef- fects among physical, biological, and chemical parameters of water chemistry (Langford 1990). Water temperature regimes dictate the types of aquatic flora and fauna present within the aquatic system, as well as influence the system’s susceptibility to parasites and disease. These regimes are commonly noted in critical habitat designations as potentially limiting to native fish populations of Southwestern streams (Federal Register 2007). Temperatures that approach the upper thermal tolerances of Southwest native fishes have been noted in Arizona streams (Deacon and Minckley 1974; USDI Geological Survey 2005). Of partic- ular interest are water temperatures for the UVR where spikedace (Meda fulgida) is imperiled. Recent fishery studies (Carveth and others 2006) suggest that na- tive fishes are sensitive to annual and large temperature fluctuations. Reduced growth rates have been reported for some species (Widmer and others 2006). The relationships between desert fishes and water temperature are unclear, especially given the assumption that they should be capable of acclimating to hot and cold temperatures common to the Southwest. State water managers rely on monitoring data to establish and validate water quality standards (Arizona Department of Environmental Quality 2002, 2007a, 2007b). Within the study area, the Arizona Department of Environmental Quality (Arizona Department of Environmental Quality 2007b) listed the headwater sec- tion of the UVR between Granite Creek and Hell Canyon as sufficiently high to support all uses attaining all uses, while the section between Perkinsville to below Camp Verde was listed as “impaired” because of sediment and turbidity. -
Annual Reportarizona YEARS 40…Of Conserving Land and Water to Benefit People and Nature
2006 annual reportArizona YEARS 40…of conserving land and water to benefit people and nature In 1966 a group of conservation-minded citizens raised money to buy the Patagonia-Sonoita Creek Preserve, and The Nature Conservancy in Arizona was born. Over the years that followed, nature preserves throughout the state were purchased by or donated to the Conservancy. They had a common focus: protecting water and VISION: We will ensure freshwater sources are restoring the health of the land. secure and sustainable in order to support our growing population and the rich diversity of life This 40th annual report documents the natural evolution of an that depends on fresh water to thrive. We will work organization whose mission calls upon us to preserve the diversity with water users, providers and those who depend on growth to create the incentives and limits that of life on Earth. We have come to cherish Arizona’s rich biological will guide future growth and create well-planned heritage. We have learned about our vital connections with communities in the face of uncertainty created by neighboring states and other countries through a system of similar securing our future global climate change. habitats or ecoregions. We are beginning to understand how special places are vulnerable to changes that occur many miles away. And, we water now know that change can be friend and foe. Today we are working at an unprecedented scale, on critical issues not recognized 40 years ago, such as Upper San Pedro Partnership Verde River Greenway With the added urgency of the first recorded no- The Conservancy sponsored field trips and provided global warming and the decline in forest health. -
Desert Sucker
Scientific Name Common Name Catostomus clarki desert sucker Bison code 010500 ____________________________________________________________ Official status Endemism ________________________ State AZ: threatened Colorado River Basin _______________________ Status/threats Introduced species and habitat alteration Distribution Presently occurs in the Virgin, Bill Williams, Salt, Verde, San Pedro, Blue, and Gila Rivers in Arizona. Occurs only in the Gila River headwaters in New Mexico and in the San Francisco River. Habitat Occupies low to high gradient riffles (0.5 to 2.0 % gradient) over pebble to cobble substrates containing water velocities of 0.5 to 1.5 cm sec. Preferred temperature of 17.5 C in Virgin River and calculated critical thermal maximums of 32-37 C. Life history and ecology Morphological complex in this species renders taxonomy difficult, however, probably more than one species exists across its range in Arizona and New Mexico. Two forms are apparent in the Virgin River basin, one in the Bill Williams basin and another form in the Bill Williams and Gila basins. Detailed genetic and morphological studies and frequent hybridization between the genera Pantosteus and Catostomus have resulted in Pantosteus being relegated to sub-generic status. Breeding Generally occurs in riffles, however, not specifically studied. Key Habitat Components: Low to high gradient riffles of moderate to swift velocity current, moderate depth (< 0.5 m), and over pebble to cobble-boulder substrate. Also in pools with moderate current. Breeding season Late winter (Jan-Feb) to early spring (March-April). Grazing effects The widespread, adaptable, and ubiquitous in addition to its generally low to high gradient riffle habitat of cobble to boulder substrates renders grazing of little potential impact to this species. -
Analyzing Rivers with Google Earth
Name____________________________________Per.______ Analyzing Rivers with Google Earth River systems exist all over the planet. You are going to examine several rivers and landforms created by rivers during this activity using Google Earth. While your iPad can view each location, you will need a laptop to use the ruler function. A B Figure 1: Meandering river terms. Image from: http://www.sierrapotomac.org/W_Needham/MeanderingRivers.htm Part I: Meandering Rivers: Figure 1 shows several terms used to describe meandering rivers. We are going to focus on wavelength, amplitude, and sinuosity. Sinuosity is the ratio of river length (distance traveled if you floated down the river) divided by straight length line (bird’s flight distance, i.e. from point A to B). The greater the number, the more tortuous (strongly meandering) the path the river takes. 1. Fly to Yakeshi, China. Just north of the city is a beautiful series of scroll bars (former point bars that have been abandoned) formed by the meandering river moving across the landscape. 1a. Describe the features you see. What “age” river is this (young, mature, old)? How are the meanders moving over time? Is the river becoming straighter or more curved? 1b. Find an area where the current river channel and clear meanders are easy to see (i.e. 49o18’30”N, 120o35’45”E). Measure the wavelength, amplitude and sinuosity of the river in this area. To measure straight line paths for wavelength, amplitude, and bird’s flight distance, go to Tools Ruler Line. Use kilometers. Click and drag your cursor across the area of interest. -
Download Paddle Map 3
Verde River Paddle Trail Highway 89A Bridge to Beasley Flat Cover Photo Courtesy of Susun McCulla Welcome to The Verde River Paddle Trail Highway 89A Bridge to Beasley Flat This paddle guide is the result of the vision and dedication of John Parsons. Many heartfelt thanks to John, his wife Susun, and his young boating partner Josh Wheeler for performing the entire field work for this guide. Special thanks to John for his decades of advocacy in support of a healthy Verde River. Photo courtesy of Gary Beverly This section of the Verde River Paddle Trail covers 31 river miles from the Highway 89A Bridgeport Bridge to Beasley Flat. The guide is composed of nine map segments, each with a corresponding descriptive narrative of GPS waypoints. A vicinity map shows how the segment maps provide coverage of each river reach, and a waypoint table provides GPS coordinates for the waypoints used in this guide. Note that much of this section of river is located on private property. Please respect the rights of these property owners during your paddle trip; it is an act of trespass to disembark and enter riverside properties. Plan your river trip accordingly and leave the river on public lands only. The Verde River is a dynamic natural resource. Water levels, channel obstructions and many other factors can change on a daily basis. River recreationists are advised to practice Safe Paddling. 1 Verde River Paddle Trail Highway 89A Bridge to Beasley Flat Safe Paddling • Never paddle alone • Inform friends and/or family of your paddling plans • Check conditions before you go • Dress appropriately for the expected weather • Wear a life jacket • Know your watercraft’s limitations • Paddle within your skill level • Avoid high, swift water • Scout any hazard about which you have doubts. -
Abstract Cenozoic Tectonism Can Be Seen in a Variety of Different Ways In
Abstract Cenozoic tectonism can be seen in a variety of different ways in the Coastal Plain of North Carolina. Using high resolution Light Detecting and Ranging digital elevation models (LiDAR), the geology of the coast can be analyzed to look for evidence supporting recent tectonism and disequilibrium. The rivers in the Coastal Plain, as well as other features, provide much evidence to support this theory. Looking at the complicated geomorphology of the rivers, particularly the Cape Fear River, gives insight to potential fault locations along the rivers. Most of the streams exhibit stream capture, another sign of disequilibrium, and the amount of stream capture was quantified on the Cape Fear River. There is a southwest migration trend in the major rivers of the Coastal Plain. While the Cape Fear Arch can explain this trend in the Cape Fear River, it does not explain the southwest migration in other rivers in the north as well. Knickpoints were found in all of the rivers in the Coastal Plain. While most of them can be associated with sea level fall or changes in underlying lithologies, there are many that are caused by tectonics. Wave-cut escarpments were once deposited horizontally in various places due to rises and falls in sea level. Elevation profiles along these scarps show a higher elevation in the north than in the south, which could be explained by uplift. This uplift would also account for the southwest migration trend in the rivers. Introduction As every geologist knows, everything on Earth is constantly changing. Mountains are being formed as well as destroyed, plates are moving, new crust is being formed as old crust is subducted and recycled, and rivers are moving. -
A Freshwater Classification of the Mackenzie River Basin
A Freshwater Classification of the Mackenzie River Basin Mike Palmer, Jonathan Higgins and Evelyn Gah Abstract The NWT Protected Areas Strategy (NWT-PAS) aims to protect special natural and cultural areas and core representative areas within each ecoregion of the NWT to help protect the NWT’s biodiversity and cultural landscapes. To date the NWT-PAS has focused its efforts primarily on terrestrial biodiversity, and has identified areas, which capture only limited aspects of freshwater biodiversity and the ecological processes necessary to sustain it. However, freshwater is a critical ecological component and physical force in the NWT. To evaluate to what extent freshwater biodiversity is represented within protected areas, the NWT-PAS Science Team completed a spatially comprehensive freshwater classification to represent broad ecological and environmental patterns. In conservation science, the underlying idea of using ecosystems, often referred to as the coarse-filter, is that by protecting the environmental features and patterns that are representative of a region, most species and natural communities, and the ecological processes that support them, will also be protected. In areas such as the NWT where species data are sparse, the coarse-filter approach is the primary tool for representing biodiversity in regional conservation planning. The classification includes the Mackenzie River Basin and several watersheds in the adjacent Queen Elizabeth drainage basin so as to cover the ecoregions identified in the NWT-PAS Mackenzie Valley Five-Year Action Plan (NWT PAS Secretariat 2003). The approach taken is a simplified version of the hierarchical classification methods outlined by Higgins and others (2005) by using abiotic attributes to characterize the dominant regional environmental patterns that influence freshwater ecosystem characteristics, and their ecological patterns and processes.