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Snohomish Estuary Wetland Integration Plan
Snohomish Estuary Wetland Integration Plan April 1997 City of Everett Environmental Protection Agency Puget Sound Water Quality Authority Washington State Department of Ecology Snohomish Estuary Wetlands Integration Plan April 1997 Prepared by: City of Everett Department of Planning and Community Development Paul Roberts, Director Project Team City of Everett Department of Planning and Community Development Stephen Stanley, Project Manager Roland Behee, Geographic Information System Analyst Becky Herbig, Wildlife Biologist Dave Koenig, Manager, Long Range Planning and Community Development Bob Landles, Manager, Land Use Planning Jan Meston, Plan Production Washington State Department of Ecology Tom Hruby, Wetland Ecologist Rick Huey, Environmental Scientist Joanne Polayes-Wien, Environmental Scientist Gail Colburn, Environmental Scientist Environmental Protection Agency, Region 10 Duane Karna, Fisheries Biologist Linda Storm, Environmental Protection Specialist Funded by EPA Grant Agreement No. G9400112 Between the Washington State Department of Ecology and the City of Everett EPA Grant Agreement No. 05/94/PSEPA Between Department of Ecology and Puget Sound Water Quality Authority Cover Photo: South Spencer Island - Joanne Polayes Wien Acknowledgments The development of the Snohomish Estuary Wetland Integration Plan would not have been possible without an unusual level of support and cooperation between resource agencies and local governments. Due to the foresight of many individuals, this process became a partnership in which jurisdictional politics were set aside so that true land use planning based on the ecosystem rather than political boundaries could take place. We are grateful to the Environmental Protection Agency (EPA), Department of Ecology (DOE) and Puget Sound Water Quality Authority for funding this planning effort, and to Linda Storm of the EPA and Lynn Beaton (formerly of DOE) for their guidance and encouragement during the grant application process and development of the Wetland Integration Plan. -
Elkhorn Slough Estuary
A RICH NATURAL RESOURCE YOU CAN HELP! Elkhorn Slough Estuary WATER QUALITY REPORT CARD Located on Monterey Bay, Elkhorn Slough and surround- There are several ways we can all help improve water 2015 ing wetlands comprise a network of estuarine habitats that quality in our communities: include salt and brackish marshes, mudflats, and tidal • Limit the use of fertilizers in your garden. channels. • Maintain septic systems to avoid leakages. • Dispose of pharmaceuticals properly, and prevent Estuarine wetlands harsh soaps and other contaminants from running are rare in California, into storm drains. and provide important • Buy produce from local farmers applying habitat for many spe- sustainable management practices. cies. Elkhorn Slough • Vote for the environment by supporting candidates provides special refuge and bills favoring clean water and habitat for a large number of restoration. sea otters, which rest, • Let your elected representatives and district forage and raise pups officials know you care about water quality in in the shallow waters, Elkhorn Slough and support efforts to reduce question: How is the water in Elkhorn Slough? and nap on the salt marshes. Migratory shorebirds by the polluted run-off and to restore wetlands. thousands stop here to rest and feed on tiny creatures in • Attend meetings of the Central Coast Regional answer: It could be a lot better… the mud. Leopard sharks by the hundreds come into the Water Quality Control Board to share your estuary to give birth. concerns and support for action. Elkhorn Slough estuary hosts diverse wetland habitats, wildlife and recreational activities. Such diversity depends Thousands of people come to Elkhorn Slough each year JOIN OUR EFFORT! to a great extent on the quality of the water. -
Geologic Site of the Month: Why Is Sebago Lake So Deep?
Why is Sebago Lake so deep? Maine Geological Survey Maine Geologic Facts and Localities February, 1999 Why is Sebago Lake so deep? 43° 51‘ 13.36“ N, 70° 33‘ 43.98“ W Text by Robert A. Johnston Maine Geological Survey, Department of Agriculture, Conservation & Forestry 1 Why is Sebago Lake so deep? Maine Geological Survey Introduction Modern geophysical equipment allows geologists to investigate previously unmapped environments, including ocean and lake floors. Recent geophysical research studied the types, composition, areal extent, and thickness of sediments on the bottom of Sebago Lake in southwestern Maine. Geologists used side- scan sonar and seismic reflection profiling to map the bottom of the lake. Approximately 58 percent of the lake bottom was imaged with side-scan sonar and over 60 miles of seismic reflection profiles were collected. This web site will discuss the findings of the seismic reflection profiling. Maine Geological Survey, Department of Agriculture, Conservation & Forestry 2 Why is Sebago Lake so deep? Maine Geological Survey Physiographic setting Sebago Lake, although second in surface area to Moosehead Lake, is Maine's deepest lake. With a water depth of 316 feet, its deepest part is 49 feet below sea level! Sebago Lake is located in southwestern Maine 20 miles northwest of Portland and 50 miles southeast of the White Mountains. It lies along the transition between the Central Highlands and the Coastal Lowlands physiographic regions of New England (Figure 1). The abrupt change in landscape can be seen in panoramic views from several vantage points near Sebago Lake. Denny, 1982 Denny, Maine Geological Survey From From Figure 1. -
Implications for Management AFRICAN GREAT LAKES
AFRICAN GREAT LAKES CONFERENCE 2nd – 5th MAY 2017, ENTEBBE, UGANDA Dynamics of Fish Stocks of Commercial Importance in Lake Victoria, East Africa: Implications for Management Robert Kayanda, Anton Taabu-Munyaho, Dismas Mbabazi, Hillary Mrosso, and Chrisphine Nyamweya INTRODUCTION • Lake Victoria with a surface area of 68,800 sqkm is the world’s second largest freshwater body • It supports one of the world’s most productive inland fisheries with the estimated total fish landings from the lake for the period of 2011 to 2014 have been about 1 million tons with a beach value increasing from about US$ 550 Million in 2011 to about US$ 840 million in 2014. • It supports about 220,000 fishers (Frame Survey 2016) • The fish stocks of Lake Victoria have changed dramatically since the introduction of Nile perch Lates niloticus during the late 1950s and early 1960s Fishery Haplochromines The Original Fish Fauna Brycinus sp Protopterus Rastrineobola Mormyrus spp Barbus spp Bagrus docmac Labeo Schilbe intermedius Oreochromis variabilis Clarias gariepinus Mormyrus spp Synodontis victoriae Oreochromis leucostictus INTRODUCTION Currently, the fisheries is dominated by four major commercial important species, these are; •Nile perch •Dagaa •Nile tilapia •Haplochromis Apart from Nile tilapia only estimated through trawl and catch surveys, the other 3 are estimated through trawl, acoustics, and catch INTRODUCTION This paper summarizes current knowledge of the status of the fish stocks and reviews the need for species specific management plans for the major commercial important fish species of Lake Victoria (Nile perch, Nile tilapia, dagaa and haplochromines). Methods • Fisheries dependent – Frame surveys – Catch assessment surveys • Fisheries independent – Acoustic – Bottom trawl Biomass and relative abundance • Total biomass from the surveys 3500 remained fairly stable over time. -
Delaware Bay Estuary Project Supporting the Conservation and Restoration Of
U.S. Fish & Wildlife Service – Coastal Program Delaware Bay Estuary Project Supporting the conservation and restoration of the salt marshes of Delaware Bay People have altered the expansive salt marshes of Delaware Bay for centuries to farm salt hay, try to control mosquitoes, create channels for boats, to increase developable land, and other reasons all resulting in restricted tidal flow, disrupted sediment balances, or increasing erosion. Sea level rise and coastal storms threaten to further negatively impact the integrity of these salt marshes. As we alter or lose the marshes we lose the valuable habitats and ecological services they provide. tidal creek - Katherine Whittemore Addressing the all-important sediment balance of salt marshes is critical for preserving their resilience. A healthy resilient marsh may be able to keep pace with erosion and sea level rise through sediment accretion and growth Downe Twsp, NJ - Brian Marsh of vegetation. However, the delicate sediment balance of salt marshes is DBEP works to support efforts to learn more about the techniques often disrupted by barriers to tidal influence and altered drainage onto and to conserve and restore salt marshes and support the populations of fish and wildlife that rely on them. We support new and off the marsh resulting in sediment ongoing coastal resiliency initiatives and coastal planning as they starved systems, excessive mudflats, or pertain to habitat restoration and conservation. We are interested increased erosion. in finding effective tools and mechanisms for conserving and restoring salt marsh integrity on a meaningful scale and support efforts that bring partners together to approach this challenge. -
The End of the Holocene Humid Period in the Central Sahara and Thar Deserts: Societal Collapses Or New Opportunities? Andrea Zerboni1, S
60 SCIENCE HIGHLIGHTS: CLIMATE CHANGE AND CULTURAL EVOLUTION doi: 10.22498/pages.24.2.60 The end of the Holocene Humid Period in the central Sahara and Thar deserts: societal collapses or new opportunities? Andrea Zerboni1, S. biagetti2,3,4, c. Lancelotti2,3 and M. Madella2,3,5 The end of the Holocene Humid Period heavily impacted on human societies, prompting the development of new forms of social complexity and strategies for food security. Yearly climatic oscillations played a role in enhancing the resilience of past societies. The Holocene Humid Period or Holocene settlements (Haryana, India), show a general changes in settlement pattern, rather than full- climatic Optimum (ca. 12–5 ka bP), in its local, trend towards desertification and higher fledged abandonment. monsoon-tuned variants of the African Humid evapotranspiration between 5.8 and 4.2 ka bP, Period (DeMenocal et al. 2000; Gasse 2000) followed by an abrupt increase in δ18O values In the SW Fazzan, the transition from the Late and the period of strong Asian southwest (or and relative abundance of carbonates, indic- Pastoral (5-3.5 ka bP) to the Final Pastoral summer) monsoon (Dixit et al. 2014), is one ative of a sudden decrease in Indian summer (3.5-2.7 ka bP) marks the ultimate adaptation of the best-studied climatic phases of the monsoon precipitations (Dixit et al. 2014). to hyperarid conditions and, later, the rise Holocene. Yet the ensuing trend towards arid- of the Garamantian kingdom (2.7-1.5 ka bP; ity, the surface processes shaping the pres- Aridification and cultural processes Mori et al. -
Rice Lake Nature Area
Rice Lake Nature Area Location: 4120 Bassett Creek Drive Nature Area Size: 9.23 Acres Description The Rice Lake Nature Area is located along the north side of Bassett Creek Drive. The nature area is within a residential neighborhood, although the woods and wetland provide more seclusion than expected for a small urban nature area. Access to the park is through a pedestrian bridge crossing of Bassett Creek, which flows from west to east. In this reach, Bassett Creek is within an incised channel and some bank erosion is present. The creek is bordered by mixed hardwood floodplain forest and hardwood swamp. Reed canary grass is present where there is sufficient clearing, but the understory can be sparse due to heavy shading. Tree removal would likely generate a flush of reed canary grass Rice Lake Nature Area can be accessed by walking an aggregate path, and a boardwalk leading to a floating dock. South Rice Pond, sometimes referred to as Rice Lake, is a shallow basin, with a wide emergent marsh fringe. Small, shallow ponds and lakes like South Rice, are somewhat unique, as they are successionally proceeding from deeper open water to wetland. That natural process can be observed from the Rice Lake Nature Area, by observing the existing habitat and surrounding areas. The Rice Lake Nature Area provides a unique opportunity to provide an unobstructed view of South Rice Pond. Because the park is dominated by wetland, access is limited to a raised trail and boardwalk. Forest and Woodlands The southern portion of the Rice Lake Nature Area is composed of a mixture of floodplain forest and hardwood swamp. -
Estuarine Wetlands
ESTUARINE WETLANDS • An estuary occurs where a river meets the sea. • Wetlands connected with this environment are known as estuarine wetlands. • The water has a mix of the saltwater tides coming in from the ocean and the freshwater from the river. • They include tidal marshes, salt marshes, mangrove swamps, river deltas and mudflats. • They are very important for birds, fish, crabs, mammals, insects. • They provide important nursery grounds, breeding habitat and a productive food supply. • They provide nursery habitat for many species of fish that are critical to Australia’s commercial and recreational fishing industries. • They provide summer habitat for migratory wading birds as they travel between the northern and southern hemispheres. Estuarine wetlands in Australia Did you know? Kakadu National Park, Northern Territory: Jabiru build large, two-metre wide • Kakadu has four large river systems, the platform nests high in trees. The East, West and South Alligator rivers nests are made up of sticks, branches and the Wildman river. Most of Kakadu’s and lined with rushes, water-plants wetlands are a freshwater system, but there and mud. are many estuarine wetlands around the mouths of these rivers and other seasonal creeks. Moreton Bay, Queensland: • Kakadu is famous for the large numbers of birds present in its wetlands in the dry • Moreton Bay has significant mangrove season. habitat. • Many wetlands in Kakadu have a large • The estuary supports fish, birds and other population of saltwater crocodiles. wildlife for feeding and breeding. • Seagrasses in Moreton Bay provide food and habitat for dugong, turtles, fish and crustaceans. www.environment.gov.au/wetlands Plants and animals • Saltwater crocodiles live in estuarine and • Dugongs, which are also known as sea freshwater wetlands of northern Australia. -
Estuary Bird Cards
TEACHER MASTER Estuary Bird Cards Great Blue Heron Osprey Willet Roseate Spoonbill Great Egret Glossy Ibis Marsh Wren Tern Brown Pelican Whooping Crane Sandpiper Avocet Woodstork Snowy Egret Black Skimmer Crested Comorant Activity 9: Bountiful Birds 10 TEACHER MASTER Estuary Habitats Salt marsh Mangrove swamp Mudflats Lagoon low tide Seagrass beds Activity 9: Bountiful Birds 11 STUDENT MASTER Great Birds of the Estuaries Estuaries actually contain a number of different habitats, each better or worse suited for different species of birds, as well as other estuary animals and plants. Here are five of the main estuary habitats: 1. A lagoon is an area of shallow, open water, separated from the open ocean by some sort of barrier, such as a barrier island. The water in a lagoon can either be as salty as the ocean or brackish. 2. A salt marsh has non-tree plants (grasses, shrubs, etc.) whose roots grow in soil acted upon by tides, but the plants are mostly never submerged. 3. The woody trees that grow in a mangrove swamp grow in soil affected by tides. Mangrove trees only grow in estuaries that never freeze. 4. Seagrass beds are always submerged underwater. Seagrass is photosynthetic, so it grows in water that is shallow and clear enough for the grass to get sunlight. Seagrass is anchored to the muddy or sandy bottom. 5. Mudflats are sometimes also called tidal flats. They are broad, flat areas of extremely fine sediment (mud) that become exposed at low tide. There are other estuary habitats. A beach or rocky shore can be part of the estuary. -
Per___1. Based on the Evidence, I Believe That the Lake
Sample: Scientific Argument NAME _________________ Per___________ 1. Based on the evidence, I believe that the lake _evaporated___. I believe this due to the evidence on card B, C and D 2. On Card B it states, “In the region where the lake is found, planetary geologists have not yet observed any summer temperatures low enough to freeze methane” This is important because This evidence refutes that the lake froze. If the temperature did not get low enough to freeze, it could not have frozen. The only other option would be that the lake evaporated 2. On Card D it states, “Summer days have more hours of sunlight. Therefore, more energy is transferred to the lake in summer than any other season. This is important because If energy is transferred into the lake, this will cause the temperature of the lake to rise. If the temperature rises, there will be more kinetic energy causing the molecules to move faster. With enough energy, evaporation can occur. With more sunlight in summer, there are more hours for the energy to enter into the lake than any other season. 2. On Card C it states, “Summer started in 2002, the lake was there in 2007, there was no lake in 2009, fall started in 2010. Seasons on Titan are just over 7 years long. This is important because Titan is cold, even in the summer, because it’s so far away from the Sun. Even though it’s cold, it is a very long summer. Summer started in 2002 and the lake was there in 2007. -
The Economics of Dead Zones: Causes, Impacts, Policy Challenges, and a Model of the Gulf of Mexico Hypoxic Zone S
58 The Economics of Dead Zones: Causes, Impacts, Policy Challenges, and a Model of the Gulf of Mexico Hypoxic Zone S. S. Rabotyagov*, C. L. Klingy, P. W. Gassmanz, N. N. Rabalais§ ô and R. E. Turner Downloaded from Introduction The BP Deepwater Horizon oil spill in the Gulf of Mexico in 2010 increased public awareness and http://reep.oxfordjournals.org/ concern about long-term damage to ecosystems, and casual readers of the news headlines may have concluded that the spill and its aftermath represented the most significant and enduring environmental threat to the region. However, the region faces other equally challenging threats including the large seasonal hypoxic, or “dead,” zone that occurs annually off the coast of Louisiana and Texas. Even more concerning is the fact that such dead zones have been appearing worldwide at proliferating rates (Conley et al. 2011; Diaz and Rosenberg 2008). Nutrient over- enrichment is the main cause of these dead zones, and nutrient-fed hypoxia is now widely at Iowa State University on January 27, 2014 considered an important threat to the health of aquatic ecosystems (Doney 2010). The rather alarming term dead zone is surprisingly appropriate: hypoxic regions exhibit oxygen levels that are too low to support many aquatic organisms including commercially desirable species. While some dead zones are naturally occurring, their number, size, and *School of Environmental and Forest Sciences, University of Washington, Seattle, Washington, USA; e-mail: [email protected] yCenter for Agricultural and Rural Development, -
Responses of Tidal Freshwater and Brackish Marsh Macrophytes to Pulses of Saline Water Simulating Sea Level Rise and Reduced Discharge
Wetlands (2018) 38:885–891 https://doi.org/10.1007/s13157-018-1037-2 ORIGINAL RESEARCH Responses of Tidal Freshwater and Brackish Marsh Macrophytes to Pulses of Saline Water Simulating Sea Level Rise and Reduced Discharge Fan Li1 & Steven C. Pennings1 Received: 7 June 2017 /Accepted: 16 April 2018 /Published online: 25 April 2018 # Society of Wetland Scientists 2018 Abstract Coastal low-salinity marshes are increasingly experiencing periodic to extended periods of elevated salinities due to the com- bined effects of sea level rise and altered hydrological and climatic conditions. However, we lack the ability to predict detailed vegetation responses, especially for saline pulses that are more realistic in nature than permanent saline presses. In this study, we exposed common freshwater and brackish plants to different durations (1–31 days per month for 3 months) of saline water (salinity of 5). We found that Zizaniopsis miliacea was more tolerant to salinity than the other two freshwater species, Polygonum hydropiperoides and Pontederia cordata. We also found that Zizaniopsis miliacea belowground and total biomass appeared to increase with salinity pulses up to 16 days in length, although this relationship was quite variable. Brackish plants, Spartina cynosuroides, Schoenoplectus americanus and Juncus roemerianus, were unaffected by the experimental treatments. Our ex- periment did not evaluate how competitive interactions would further affect responses to salinity but our results suggest the hypothesis that short pulses of saline water will increase the cover of Zizaniopsis miliacea and decrease the cover of Polygonum hydropiperoides and Pontederia cordata in tidal freshwater marshes, thereby reducing diversity without necessarily affecting total plant biomass.