Floating Wetlands for Urban Stormwater Treatment Chih-Yu

Total Page:16

File Type:pdf, Size:1020Kb

Floating Wetlands for Urban Stormwater Treatment Chih-Yu Floating wetlands for urban stormwater treatment Chih-Yu Wang Dissertation submitted to the faculty of the Virginia Polytechnic Institute and State University in partial fulfillment of the requirements for the degree of Doctor of Philosophy In Biological Systems Engineering David J. Sample, Chair Susan D. Day Daniel L. Gallagher Thomas J. Grizzard Theresa M. Thompson October 29, 2013 Virginia Beach, VA Keywords: Retention ponds, Nutrient control, Performance assessment, Nutrient harvest, Sustainability. Copyright © 2013 by Chih-Yu Wang Floating wetlands for urban stormwater treatment Chih-Yu Wang ABSTRACT A floating treatment wetland (FTW) is an ecological approach which seeks to reduce point and nonpoint source pollution by installing substrate rooted plants grown on floating mats in open waters. While relatively novel, FTW use is increasing. A review of literature identified several research gaps, including: (1) assessments of the treatment performance of FTWs; (2) evaluations of FTWs in the U.S., particularly within wet ponds that receive urban runoff; and (3) plant temporal nutrient distribution, plant growth rate, and the long-term persistence of the FTWs in temperate regions with periodic ice encasement. An assessment model, i-FTW model, was developed, and its parameter s fitted based on data from 14 published FTW studies in the first research topic. The estimated median FTW apparent uptake velocity with 95% confidence interval were 0.048 (0.018 – 0.059) and 0.027 (0.016 – 0.040) m/day for total phosphorus (TP) and total nitrogen (TN), respectively. The i- FTW model provided a more accurate prediction in nutrient removal than two common performance metrics: removal rate (mg/m2/day) and removal efficiency (%). In the second research topic, the results of a mesocosm experiment indicated that FTWs with 61% coverage, planted with pickerelweed (Pontederia cordata L.) or softstem bulrush (Schoenoplectus tabernaemontani), significantly improved TP and TN removal efficiency of the control treatment by 8.2% and 18.2%, respectively. The pickerelweed exhibited significantly higher phosphorus and nitrogen removal than the softstem bulrush when water temperatures were greater than 25ºC . Field observations in the third research topic found that pickerelweed demonstrated higher phosphorus removal performance (7.58 mg/plant) than softstem bulrush (1.62 mg/plant). Based on the observed seasonal changes in phosphorus distribution, harvest of above-ground vegetation is recommended to be conducted twice a year in June and September. Planted perennial macrophytes successfully adapted to stresses of the low dissolved oxygen (DO) concentrations (minimum: 1.2 mg/L), ice encasement, and relatively low nutrient concentrations in the water (median: 0.15 mg/L TP and 1.15 mg/L TN). Systematic observation of wildlife activities indicated eight classes of organisms inhabiting, foraging, breeding, nursing, or resting in the FTWs. Recommendations for FTW design and suggestions for further research are made based upon these findings. Acknowledgements I would like to express my sincere appreciation to my committee members for their guidance throughout my Ph.D. studies, which allowed me to discover the findings contained in this dissertation and contribute to the advancement of science. The most important value I received is the spirit of the scientific research within higher education that I experienced through individual discussions and regular group meetings with committee members in my time at Virginia Tech. I wish to express immense gratitude to Dr. David J. Sample. As my academic advisor, he gave me a great research opportunity, provided me continuous support and encouragement, and guided me through the course that I could complete the work. I am particularly grateful to Dr. Susan D. Day, who shared her expertise in the areas of macrophytes and enriched this portion of my research; to Dr. Daniel L. Gallagher, who refreshed my understanding about the statistics and teaches a very practical statistical class with enjoyable mid- and final-exam questions; to Dr. Thomas J. Grizzard, who provided ideas to develop the assessment model and supported experimental analyses; to Dr. Theresa M. Thompson, who educated me in the spirit of scientific research and provided me the opportunity to participate in a stream restoration project in Blacksburg. I am sincerely thankful for the committee members’ devotion of their valuable time and efforts to educate and prepare me for responsibilities as a scientist, a mentor, and a member of the society. Special thanks go to Dr. Adil N. Godrej, Dr. Jim S. Owen, Dr. Laurie J. Fox, Haibo Zhang, Julie Brindley, Dongmei Wang, Joan Wirt, and reviewers of Ecological Engineering and Journal of Environmental Management for their support, advice and expertise throughout this research. Additionally, I wish to express my appreciation for the support from the Department of Biological System Engineering (BSE) and the department’s Ph.D. student training system, including the BSE seminar presentation with written feedback, and financial sponsorship for professional travels, such as conference presentations. Funding for this research was partially provided by the National Fish and Wildlife Foundation and City of Fairfax; additional funding was also provided by the College of Agriculture, Integrated Research/Extension Grants Program. Additional support was provided by Adrian Fremont of City of Fairfax and William Lucas of Integrated Land Management, Inc. for the Ashby Pond retrofit design and execution. iii I would like to thank my friends and the staff of the Occoquan Watershed Monitoring Laboratory (OWML): Dr. Justin Bartlett, Dr. Francisco Cubas, Dr. Jia Liu, Dr. Saurav Kumar, , Barbara Angelotti, Harry Post, Dongmei Wang, Curt Eskridge, Mike Gaal, Doug Holladay, Paul Le Bel, Mark Lucas, Phil Spellerberg, Woody Underwood, and Joan Wirt. Although I am far from my hometown, Taiwan, I was enjoyed my life in the U.S. in particular because I worked at the OWML with a family-like atmosphere built by everyone in the team. Finally, I would like to dedicate this work to my wife, Chia-Yu Chang, and my family. With their perpetual support, I have been able to focus on pursuing my goals. Chia-Yu, especially, who postponed her career and chose to accompany me and stay by my side in the U.S. Her love and support motivated me to complete this work and move forward. iv Table of Contents Chapter 1. Introduction ................................................................................................................. 1 1.1 Urban stormwater pollution ............................................................................................. 1 1.2 Study area......................................................................................................................... 2 1.3 Research problems and goals ........................................................................................... 4 1.4 Study Topics .................................................................................................................... 7 1.4.1 Topic I .................................................................................................................. 7 1.4.2 Topic II................................................................................................................. 7 1.4.3 Topic III ............................................................................................................... 7 1.5 References ........................................................................................................................ 8 Chapter 2. Literature review ....................................................................................................... 11 2.1 Water purification mechanisms of FTWs ...................................................................... 12 2.1.1 Macrophytes ....................................................................................................... 12 2.1.2 Root systems ...................................................................................................... 13 2.1.3 Microorganisms ................................................................................................. 14 2.1.4 Raft ..................................................................................................................... 14 2.2 Advantages of FTWs ..................................................................................................... 15 2.2.1 Environmental adaptability and variety of applications .................................... 15 2.2.2 Ease of development and management .............................................................. 15 2.2.3 Nutrients recycling and economic returns ......................................................... 16 2.2.4 Economical and natural pollution control technology ....................................... 17 2.3 Disadvantages of FTWs ................................................................................................. 18 2.3.1 Chemical limitations .......................................................................................... 18 2.3.2 Physical limitations ............................................................................................ 19 2.3.3 Biological limitations ......................................................................................... 19 2.4 Applications and Studies of FTW .................................................................................. 20 2.5 References
Recommended publications
  • Old Town Pond & Wickapogue Pond
    Old Town Pond & Wickapogue Pond Village of Southampton, NY 2020 Management Plan Three integrated strategies to restore Old Town Pond & Wickapogue Pond Improve Pond Water Quality Increase Stormwater Drainage Water Quality Study & Reduce Nutrient Pollution Algae Harvester Old Town Pond Green Infrastructure: Air Bubblers Bioswales for Continuous Monitoring Old Town Pond - North & South Dredge Sediments I/A Septic Upgrades Reduce Fertilizer/Chemical Use Accelerate Enhancements to Shoreline & Natural Buffer Areas Waterfront Natural Buffer Areas Remove Invasive Vegetation Constructed Treatment Wetland & Repair Dock/Walkway for Old Town Pond – North Grass-PAVE2 Permeable Parking Areas for Old Town Pond - East Summary of Old Town Pond & Wickapogue Pond Management Recommendations The Old Town Pond & Wickapogue Pond 2020 Management Plan, created by the Southampton Village Clean Water Committee, was approved and adopted by the Southampton Village Mayor and Trustees on December 10, 2020. Old Town Pond Overview The New York State Department of Environmental Conservation (DEC), Shinnecock Bay/Atlantic Ocean Watershed report, includes a fact sheet for Old Town Pond, an 8.5-acre pond which is assessed as an impaired waterbody. Recreational uses are considered to be impaired by frequent to persistent occurrences of harmful algal blooms. Aquatic life may also be impacted by resulting low dissolved oxygen in the pond. Nonpoint stormwater runoff, agricultural activity and residential onsite septic systems are suspected sources of pollutants. Old Town Pond was sampled in 2015 by SUNY Stony Brook as part of a harmful algae bloom collaborative with the DEC, Division of Water. Nonpoint stormwater runoff, agricultural activity and residential onsite septic systems are suspected sources of nutrients that are thought to be contributing to the algal blooms and could be resulting in low dissolved oxygen in the pond.
    [Show full text]
  • Enhancement of New York Harbor Estuaries and Ecological Systems Proposals for Environmental Restoration
    ENHANCEMENT OF NEW YORK HARBOR ESTUARIES AND ECOLOGICAL SYSTEMS PROPOSALS FOR ENVIRONMENTAL RESTORATION CUISD HONORABLE MENTION SUBMISSION TO AN OPEN INTERNATIONAL DESIGN COMPETITION TO ENVISION WATER AS THE THE SIXTH BOROUGH OF NEW YORK CITY MAY, 2011 Institute for Sustainable Design The Cooper Union for the Advancement of Science and Art PREPARED BY Cooper Square New York, NY 10003-7120 THE COOPER UNION INSTITUTE www.cooper.edu/isd FOR SUSTAINABLE DESIGN 2 3 ENHANCEMENT OF NEW YORK HARBOR ESTUARIES AND ECOLOGICAL SYSTEMS PROPOSALS FOR ENVIRONMENTAL RESTORATION OPEN INTERNATIONAL DESIGN COMPETITION TO ENVISION WATER AS THE THE SIXTH BOROUGH OF NEW YORK CITY MAY, 2011 PREPARED BY THE COOPER UNION INSTITUTE FOR SUSTAINABLE DESIGN INTRODUCTION ENHANCEMENT OF NEW YORK HARBOR THE DEMANDS TO BE MET ESTUARIES AND ECOLOGICAL SYSTEMS ARE MANY: To transform the harbor and estuaries to meet the 1. Rising sea levels, temperature rise and increasing changing demands of the coming decades and to offer a storm intensity due to climate change richer and more ecologically integrated urban environment 2. More robust storm surges and coastal flood potential will require planning approaches that employ various 3. Increased population in NYC needing the benefits of strategies and support interventions at multiple scales. natural systems. 4. Increased need for soft path servicing, ecological Navigational Dredging Policy should be made to concentrate treatment of wastewater and passive water quality maritime industry and shipping at critical zones. The overall improvement methods. amount of channelization should be reduced to support functioning 5. Need for increased natural bio-diversity and re- navigational routes and maintain active berths (with an allowance establishment of wetland habitats.
    [Show full text]
  • Status of the Aquatic Plant Maintenance Program in Florida Public Waters
    Status of the Aquatic Plant Maintenance Program in Florida Public Waters Annual Report for Fiscal Year 2006 - 2007 Executive Summary This report was prepared in accordance with §369.22 (7), Florida Statutes, to provide an annual assessment of the control achieved and funding necessary to manage nonindigenous aquatic plants in intercounty waters. The authority of the Department of Environmental Protection (DEP) as addressed in §369.20 (5), Florida Statutes, extends to the management of nuisance populations of all aquatic plants, both indigenous and nonindigenous, and in all waters accessible to the general public. The aquatic plant management program in Florida’s public waters involves complex operational and financial interactions between state, federal and local governments as well as private sector compa- nies. A summary of plant acres controlled in sovereignty public waters and associated expenditures contracted or monitored by the DEP during Fiscal Year 2006-2007 is presented in the tables on page 42 of this report. Florida’s aquatic plant management program mission is to reduce negative impacts from invasive nonindigenous plants like water hyacinth, water lettuce and hydrilla to conserve the multiple uses and functions of public lakes and rivers. Invasive plants infest 95 percent of the 437 public waters inventoried in 2007 that comprise 1.25 million acres of fresh water where fishing alone is valued at more than $1.5 billion annually. Once established, eradicating invasive plants is difficult or impossible and very expensive; therefore, continuous maintenance is critical to sustaining navigation, flood control and recreation while conserving native plant habitat on sovereignty state lands at the lowest feasible cost.
    [Show full text]
  • Floating Wetland Islands Implementation and Biodiversity Assessment in a Port Marina
    water Article Floating Wetland Islands Implementation and Biodiversity Assessment in a Port Marina 1, , 1,2, 1 1,2 Cristina S. C. Calheiros * y , João Carecho y, Maria P. Tomasino , C. Marisa R. Almeida and Ana P. Mucha 1,2 1 Interdisciplinary Centre of Marine and Environmental Research (CIIMAR/CIMAR), University of Porto, Novo Edifício do Terminal de Cruzeiros do Porto de Leixões, Avenida General Norton de Matos, S/N, 4450-208 Matosinhos, Portugal; [email protected] (J.C.); [email protected] (M.P.T.); [email protected] (C.M.R.A.); [email protected] (A.P.M.) 2 Faculty of Sciences, University of Porto, Praça de Gomes Teixeira, 4099-002 Porto, Portugal * Correspondence: [email protected] These authors contributed equally to this manuscript. y Received: 27 October 2020; Accepted: 18 November 2020; Published: 21 November 2020 Abstract: Floating wetland islands (FWI) are considered nature-based solutions with great potential to promote several ecosystem services, such as biodiversity and water quality enhancement through phytoremediation processes. To our knowledge, the present work is the first to scientifically document the in-situ establishment of an FWI in a seawater port marina. The establishment and performance of a cork floating platform with a polyculture (Sarcocornia perennis, Juncus maritimus, Phragmites australis, Halimione portulacoides, Spartina maritima, Limonium vulgare) was evaluated. The diversity of organisms present in the FWI was undertaken based on the macrofauna assessment, taking into consideration marine water characterization, with a focus on hydrocarbons. Microbial communities were assessed based on metabarcoding approach to study 16S rRNA gene from environmental DNA retrieved from biofilm (from the planting media), marine biofouling (from the submerged platform) and surface marina water.
    [Show full text]
  • Response of Fish Populations to Floating Streambed Wetlands
    Fish and Floating Streambed Wetlands . Neal and Lloyd Response of Fish Populations to Floating Streambed Wetlands J. Wesley Neal, Mississippi State University, Box 9690, Department of Wildlife, Fisheries and Aquaculture, Mississippi State, MS 39762 M. Clint Lloyd 1, Mississippi State University, Box 9690, Department of Wildlife, Fisheries and Aquaculture, Mississippi State, MS 39762 Abstract: A new tool to provide wetland services is the floating streambed wetland (FSW), an active hydroponic system consisting of a polymer matrix floating substrate in which living plants are established. Water is circulated from beneath the FSW and across a streambed on the upper FSW surface, coming into contact with biofilms attached to the polymer matrix and associated root structures. Research has shown that FSW technology is efficient in removing nutrients and water contaminants, and recent manufacturer reports claim that FSW technology may also increase total fish biomass in small water bodies. We evaluated this claim using a replicated small (526 m 2) pond experiment and FSWs that covered 2.3% of pond surface area. FSWs were installed and planted in August 2013, and ponds were stocked at equal densities with bluegill (Lepomis macrochirus) in October 2013 and large- mouth bass (Micropterus salmoides) in August 2014; populations were allowed to develop naturally prior to harvest in April 2016. Total fish biomass at time of harvest was 19.9% greater in ponds with FSWs than in control ponds. No differences in growth rates were observed for either species. This exploratory study suggested that FSWs can increase fish production in ponds, but further study is warranted. The high cost of FSWs would likely limit their use for strictly fisheries management purposes.
    [Show full text]
  • Uros Hand Made Reed Floating Islands
    Uros hand made reed floating islands A proved ancient technique Today a closed cycle in practice to learn from Tomorrow an innovative development Rocío Torres Méndez Because of global warming, rising sea levels and the running out of fossil fuels, it is important to look for sustainable adaptable solutions. Therefore special attention should be given to the potential of floating reeds in construction. This paper is about a closed cycle example in practice, to learn from. It tells the history of a millenary South American civilization named Uros. It gives an overview of sustainable daily practices of the Uros - who live on floating organic hand made islands on the cold waters of Lake Titicaca at 3810 m above sea level in Puno, Peru - and their potential for future innovative developments. The objective of this paper is to highlight the importance of researching the Totora plant’s floating properties, which will give us insights into its possible diverse applications as a floating material of construction. This study bridges science with traditional knowledge, an inspiring lesson for developing innovative ideas. 1 Location: Puno- Peru Figure 1 : Islands located at five kilometers east from Puno port at 3810m above sea level Source: Google earth The Totora plant This paper is about the Totora plant that grows in Titicaca Lake. Its scientific name is Schoenoplectus californicus ssp. tatora. Totora is an aquatic plant which grows in humid places, wetlands, along rivers and lakes. This plant has a long stem (400 cm long approximately) and its stem section has a circular shape (d =1.5 cm aprox).
    [Show full text]
  • Stormwater Floating Islands (SFI) and Thus Helping to Reduce the Nutri- Ents and Pollutants Before the Outfall
    STORMWATER FLOATING ISLANDS Case study INNOHULE LAHTI UNIVERSITY OF APPLIED SCIENCES Master in Engineering Urban Sustainability Autumn 2018 Waseem Sukkari Abstract Author(s) Type of publication Published Sukkari, Waseem Master’s thesis Autumn 2018 Number of pages Appendices 66 pages 16 pages Title of publication Stormwater Floating Island Case Study INNOHULE Name of Degree Master in Engineering Abstract Stormwater management faces many problems and challenges. One of these challenges is the nutrients and pollutants that accumulate in the stormwater and are discharged into the water bodies like rivers and lakes, which negative- ly affect the environment, water quality, and ecosystem of the water bodies. This thesis discusses the importance of enhancing the work of wetlands by adding Stormwater Floating Islands (SFI) and thus helping to reduce the nutri- ents and pollutants before the outfall. An experiment project INNOHULE has been carried out to obtain preliminary results regarding nutrients removal and data on native plants that have the ability to adapt to the new submerged condition and the ability to survive the extreme low temperature winter. Also, water tests were conducted to ascertain the efficiency of the SFI concept 3− − for the following nutrients: Phosphate PO₄ , Nitrate NO₃⁻, Nitrite NO2 , and Ammonium/Ammonia NH₄⁺ / NH₃. Finally, the concept of SFI found that it can be applied in Finland, as well as a good variety of native plants that can tolerate the new submerged condition in a SFI. The concept of SFI can help mitigate nutrients and pollutants from stormwater wetlands. During the INNOHULE project; recycled materials were used to build the SFIs, and many designs succeed to achieve the purpose role.
    [Show full text]
  • Best of Peru
    Best of Peru — Machu Picchu, Sacred Valley of the Incas, Lake Titicaca, Floating Islands of Uros, Arequipa, Colca Canyon — TOUR DETAILS Best of Peru Highlights • Price: $3,295 USD • Machu Picchu • Discounts: • Sacred Valley of the Incas • 5% - Returning Volant Customer • Vistadome Train Ride, Andes Mountains • Cusco, 16th century Spanish Culture • Duration: 15 days • Puerto Maldonado • Date: April/May 2018 • Tambopata Reserve • Difficulty: Easy • Amazon River • Manu National Park Inclusions • Puno, Historic Plaza de Armas • Lake Titicaca • All internal flights (while on tour) • Floating Islands of Uros • All scheduled accommodations (2-3 star) • Arequipa, Historic Old Town • All scheduled meals • Colca Canyon • Transportation throughout tour • Lima, Historic Old Town • Airport transfers • Machu Picchu entrance fee Exclusions • Vistadome Train Ride, Peru Rail • International airfare (to and from Lima, Peru) • Luxury tour bus ride to Puno • Entrance fees to museums and other attractions • Personal guide throughout tour not listed in inclusions • Personal items: Laundry, shopping, etc. ITINERARY Best of Peru - 15 Days / 14 Nights Itinerary - DAY ACTIVITY LOCATION - MEALS • Arrive: Jorge Chavez International Airport (LIM), Lima, Peru Lima, Peru 1 • Transfer to hotel • Miraflores and Pacific coast Dinner Lima, Peru • Tour Lima’s Historic District 2 • San Francisco Monastery & Catacombs, Plaza Mayor, Lima Cathedral, Government Palace Breakfast, Lunch, Dinner • Flight to Puerto Maldonado Puerto Maldonado • Transfer to hotel 3 • Leisurely afternoon
    [Show full text]
  • Surprising Peru Old World Traditions
    GO solo SURPRISING PERU OLD WORLD TRADITIONS. NEW WORLD adventure. May 7 – 21, 2019 Join other intrepid travellers and check this unforgettable land from your bucket list. Fly over Nazca’s mysterious desert geoglyphs. Glide on tranquil water to the floating islands of Uros on Lake Titicaca. Ascend to the seat of the Inca empire at Machu Picchu. And much more. The wonders of Peru and all its diversity abound on this 15-day epic journey. ITINERARY Lima I Paracas I Nazca I Arequipa I Cuzco I Sacred Valley I Aguas Calientes I Machu Picchu I Cuzco I Puno I Lake Titicaca May 7 – Arrive Lima and transfer to your hotel. May 8 – Drive south along the Pacific Coast to Paracas. Enjoy a Pisco Sour and a welcome dinner tonight. (B/D) HIGHLIGHTS May 9 – Take a boat trip to the Ballestas Islands; home to Girl on Uros floating island, Puno thousands of birds and seal colonies. Visit Tacama Winery and then continue to Nazca. (B) INCLUSIONS • 14 nights in 3-star accommodations May 10 – This morning fly over the incredible Nazca Lines; the • Daily breakfast, 6 lunches and 4 dinners enormous figures drawn on the desert floor about 2,000 • Domestic flights within Peru years ago. (B/D) • Sightseeing and admissions as per the itinerary May 11 – Travel from Nazca to Arequipa. (B/L) • Transfers and transportation by private vehicle with driver/guide – Enjoy a half-day city tour of Arequipa including viewing May 12 Crystal Pajunen the volcanoes Misti, Chachani and Pichu Pichu. Later learn • Gratuities for drivers, guides and porterage how to make local dishes during a cooking class.
    [Show full text]
  • Physical and Vegetative Characteristics of Floating Islands
    J. Aquat. Plant Manage. 39: 107-111 Physical and Vegetative Characteristics of Floating Islands CRAIG T. MALLISON1, RANDALL K. STOCKER2 AND CHARLES E. CICHRA3 ABSTRACT definition includes small (less than 0.01 ha) free-floating is- lands and extensive, stationary, vegetated mats which may Due to variable biomass and volume among floating is- cover hundreds of hectares of water. Although floating is- lands (or tussocks), efficiency of management is often diffi- lands often contain floating aquatic plant species such as wa- cult to predict before activities occur. Objectives were to ter hyacinth (Eichhornia crassipes (Mart.) Solms.) and frog’s- identify major types of floating islands based on dominant bit (Limnobium spongia (Bosc.) Steud.), they are not made up vegetation, and to evaluate physical and vegetative character- entirely of floating aquatic vegetation. istics of each type. In October 1997, analysis of 116 floating Interest in floating islands in Florida lakes has recently in- islands on Orange Lake, Florida revealed five major types: 1) creased due to problems associated with their accumulation Cuban bulrush (Scirpus cubensis Poepp. and Kunth.) and wa- along shorelines, which may block lake-access points (docks ter pennywort (Hydrocotyle spp.); 2) grasses; 3) bur marigold and boat ramps), interfere with recreation and navigation, (Bidens spp.), cattail (Typha latifolia L.), and smartweed and shade out and displace desirable submersed and emer- (Polygonum spp.); 4) facultative (plants that occur in wetlands gent vegetation (Hujik 1994, Mallison and Hujik 1999). Wa- and uplands); and 5) pickerelweed (Pontederia cordata L.). In ter below extensive stands of floating islands is often low in November 1997, three floating islands per type were exam- dissolved oxygen and high in organic matter, thus water qual- ined to evaluate size, composition and coverage of plant ity is poor for fisheries habitat (Alam et al.
    [Show full text]
  • Constructed Floating Wetlands: a Review of Research, Design, Operation and Management Aspects, and Data Meta-Analysis ⇑ Natalia Pavlineri A,B, Nikolaos Th
    Chemical Engineering Journal 308 (2017) 1120–1132 Contents lists available at ScienceDirect Chemical Engineering Journal journal homepage: www.elsevier.com/locate/cej Review Constructed Floating Wetlands: A review of research, design, operation and management aspects, and data meta-analysis ⇑ Natalia Pavlineri a,b, Nikolaos Th. Skoulikidis a, Vassilios A. Tsihrintzis b, a Institute of Inland Waters, Hellenic Centre for Marine Research, Greece b Centre for the Assessment of Natural Hazards and Proactive Planning & Laboratory of Reclamation Works and Water Resources Management, Department of Infrastructure and Rural Development, School of Rural and Surveying Engineering, National Technical University of Athens, Zografou 157 80, Athens, Greece highlights graphical abstract Constructed Floating Wetlands. Water and wastewater treatment. Review of research, design, operation and management. article info abstract Article history: This paper summarizes the state-of-the-art on Constructed Floating Wetlands (CFWs). An attempt has Received 26 July 2016 been made here to collect and organize current literature and provide an insight to most topics of the Received in revised form 27 September ongoing scientific conversation on CFWs. Several issues are discussed such as applications, construction 2016 materials, vegetation species, mechanisms for pollutant removal and management strategies. Raw data Accepted 28 September 2016 were extracted from studies and were imposed to statistical analysis in order to reveal correlations Available online 30 September 2016 (Spearman’s r coefficient) between total nitrogen (TN), total phosphorus (TP) and ammonium nitrogen (NH+-N) concentration reduction and several operational or design parameters, e.g., vegetation aerial Keywords: 4 coverage, water depth, initial loading, Hydraulic Loading Rate (HLR) and Hydraulic Retention Time Constructed Floating Wetlands Natural water/wastewater treatment (HRT).
    [Show full text]
  • Cleveland Metroparks Board of Park Commissioners Work Session
    Cleveland Metroparks Board of Park Commissioners Work Session 24 Strategic Plan Goals Emerald Necklace Endowment Fund — Individual 2010 2011 2012 2013 2014 2015 2016 Total Individual Giving $1,838,677 $99,811 $136,291 $252,512 $236,735 $261,062 $643,507 $3,468,595 Total Donors 434 436 497 414 920 645 534 3,880 High Gift $1,727,066 $26,507 $34,500 $26,477 $60,000 $47,488 $300,000 $2,222,038 Low Gift $5 $5 $5 $5 $5 $5 $5 $5 Average $4,237 $229 $274 $610 $257 $405 $1,205 $894 2010-2016 Individual Giving Funding by Area Total: $897,908 Conservation Capital Projects Education Nature Centers Trails Rangers Funding by Area 2010 2011 2012 2013 2014 2015 2016 Total Conservation $24,200 $23,400 $42,800 $39,200 $50,700 $47,164 $70,022 $297,486 Capital Projects $19,318 n/a n/a $65,000 $5,000 $57,672 $77,595 $224,585 Education $18,000 $21,640 $13,750 $17,090 $13,060 $13,978 $25,397 $122,915 Nature Centers n/a n/a $4,900 $15,100 $14,600 $11,256 $7,125 $52,981 Trails $1,400 $3,300 $11,500 $41,600 $28,100 $38,436 $55,367 $179,703 Rangers $8,000 $280 $2,800 $1,800 $2,650 $2,092 $2,616 $20,238 Total $70,918 $48,620 $75,750 $179,790 $114,110 $170,598 $238,122 $897,908 2 23 Emerald Necklace Endowment Fund 2010-2016 Grant & Donation Summary The current value of the Emerald Necklace Endowment Fund is $3,266,123.
    [Show full text]