This document discusses improving storm water management through the use of permeable pavements. It provides background on the negative environmental impacts of impervious surfaces and the challenges they pose for city officials. It then describes permeable interlocking concrete pavements as a best management practice that can help mitigate these issues. Specifically, it allows storm water to infiltrate the pavement and base layers, recharging groundwater and reducing runoff. The document provides details on the design, installation, and performance of permeable interlocking concrete pavements as an effective sustainable solution.
Storm water is not only collected from the roof it's also collected from the roads, footpath, parking, lawns and open spaces etc.. and their is four types from water is collected roof water,surface water,sub-drain and soil drain. And what are the various components for collection are described here.
Controlling Roadway Soil Erosion with Compostspickell
In this presentation given to the Maryland Highway Administration's Recycled Materials Task Force, Brenda Platt outlines how compost use can control soil erosion.
W.A.R.(waterabsorbingroad): New technique for road construction using permeab...SaurabhPawar76
This document presents a study on a new technique called Water Absorbing Road (W.A.R.) that uses permeable pavement for road construction. The study examines the use of permeable concrete, asphalt, and pavers that allow stormwater to enter and be filtered. Benefits include reduced runoff and flooding, improved water quality by trapping pollutants, and increased road safety and durability. The study tests compressive strengths of permeable and conventional concrete. Maintenance and costs are also compared. The research methodology examines hydrological and structural design. Potential benefits are groundwater recharge and reduced need for drainage systems, while challenges include needing specialized construction and potential clogging over time.
Klingbeil, R., 2012. Water Management Challenges Under Drought Conditions. Presentation at the "Consensus Building and Awareness Workshop, Iraq Drought Risk Management Project", joint workshop of GoI, UNDP, UNESCO and UN ESCWA, 26-28 Mar 2012, Beirut, Lebanon.
This document provides a technical report on proposed solutions to surface water drainage problems in Diepsloot, South Africa. It discusses the current issues with insufficient stormwater infrastructure and proposes investigating permeable paving, rainwater harvesting, and swales as potential sustainable urban drainage systems. Permeable paving allows water to infiltrate through paved surfaces and includes considerations for design, construction, and maintenance. Rainwater harvesting focuses on collecting roof runoff but may not be practical for the informal housing in Diepsloot. The report will conceptually design and analyze a selected solution.
The document discusses reservoir planning and gravity dams. It covers topics like reservoir investigations, site selection, zones of storage, yield and capacity calculations. It also discusses types of dams, selection of dam type and site, and forces acting on gravity dams. Gravity dams are described as structures that resist forces through their own weight. Key forces on gravity dams include water pressure, uplift pressure, earthquake pressure, and more.
Storm water is not only collected from the roof it's also collected from the roads, footpath, parking, lawns and open spaces etc.. and their is four types from water is collected roof water,surface water,sub-drain and soil drain. And what are the various components for collection are described here.
Controlling Roadway Soil Erosion with Compostspickell
In this presentation given to the Maryland Highway Administration's Recycled Materials Task Force, Brenda Platt outlines how compost use can control soil erosion.
W.A.R.(waterabsorbingroad): New technique for road construction using permeab...SaurabhPawar76
This document presents a study on a new technique called Water Absorbing Road (W.A.R.) that uses permeable pavement for road construction. The study examines the use of permeable concrete, asphalt, and pavers that allow stormwater to enter and be filtered. Benefits include reduced runoff and flooding, improved water quality by trapping pollutants, and increased road safety and durability. The study tests compressive strengths of permeable and conventional concrete. Maintenance and costs are also compared. The research methodology examines hydrological and structural design. Potential benefits are groundwater recharge and reduced need for drainage systems, while challenges include needing specialized construction and potential clogging over time.
Klingbeil, R., 2012. Water Management Challenges Under Drought Conditions. Presentation at the "Consensus Building and Awareness Workshop, Iraq Drought Risk Management Project", joint workshop of GoI, UNDP, UNESCO and UN ESCWA, 26-28 Mar 2012, Beirut, Lebanon.
This document provides a technical report on proposed solutions to surface water drainage problems in Diepsloot, South Africa. It discusses the current issues with insufficient stormwater infrastructure and proposes investigating permeable paving, rainwater harvesting, and swales as potential sustainable urban drainage systems. Permeable paving allows water to infiltrate through paved surfaces and includes considerations for design, construction, and maintenance. Rainwater harvesting focuses on collecting roof runoff but may not be practical for the informal housing in Diepsloot. The report will conceptually design and analyze a selected solution.
The document discusses reservoir planning and gravity dams. It covers topics like reservoir investigations, site selection, zones of storage, yield and capacity calculations. It also discusses types of dams, selection of dam type and site, and forces acting on gravity dams. Gravity dams are described as structures that resist forces through their own weight. Key forces on gravity dams include water pressure, uplift pressure, earthquake pressure, and more.
NY: A Green Infrastructure Approach - Onondaga Creek Water QualitySotirakou964
This document summarizes a report on improving water quality in Onondaga Creek through green infrastructure approaches. It provides background on combined sewer overflows polluting the creek and discusses planning efforts to reduce stormwater runoff volumes. The report selects a site for modeling green infrastructure techniques, including bioswales, curb cuts, rain gardens, blue roofs, and permeable surfaces. It analyzes costs and recommends the designed approaches as sustainable and cost-effective alternatives to traditional sewer infrastructure expansion.
Water resources engineering is concerned with controlling water quantity, quality, timing and distribution to meet human and environmental needs. It includes the disciplines of hydrodynamics, hydraulics, and hydrology. Water resources include surface water, groundwater, oceans, rivers, lakes, glaciers and snowfields. Water circulates through the hydrologic cycle of precipitation, runoff, storage, and evapotranspiration. Water resources development through engineering intervention is needed to meet uneven human demand, but must be done sustainably to ensure future generations' access to water without compromising environmental quality.
The document discusses changing stormwater regulations in Connecticut. Municipalities are increasingly requiring low impact development (LID) techniques to reduce stormwater pollution from development. LID aims to reduce impervious surfaces and runoff volumes to lower pollutant loads through techniques like bioretention basins, narrower roads, and permeable pavement. The document provides examples of LID projects and maintenance best practices to meet water quality goals and comply with new regulations.
This document provides information on sustainable stormwater management. It begins with an introduction on stormwater and the need for management. Examples of stormwater management techniques are then presented, including rain gardens, bioretention areas, vegetated swales, green roofs, and porous pavement. The installation processes for rain gardens and bioretention areas are described in multiple steps. Advantages and disadvantages of stormwater management are listed. The document concludes with references and appendices.
Watershed Managment by Muhammad Qasim & Aroj BashirMuhammad Qasim
This document discusses watershed management and its importance. It defines a watershed as an area where all water flows to a common outlet. It describes the key features of watersheds including size, terrain, soil type, and drainage divides. It outlines how human activities like pollution, overpopulation, and deforestation impact watersheds. The document advocates for watershed management to regulate pollution and monitor watershed health. It provides an example of a project improving sub-watershed management and environmental awareness in Pakistan's Ayubia National Park to contribute to sustainable water flows.
Gray vs. Green: The Role of Watershed-scale Green Infrastructure Systems for ...Mcrpc Staff
This document discusses the role of green infrastructure systems for managing wastewater at a watershed scale. It begins by outlining the historical patterns of water movement through uplands and lowlands, and how contemporary development has reversed these patterns. It then describes various green infrastructure strategies that can replicate natural hydrology, including green roofs, porous pavements, bio-retention systems, rainwater harvesting, wastewater recycling, and native landscaping. The document provides examples of these strategies and concludes by discussing a new paradigm in wastewater treatment using lagoons and floating mats of bacteria to polish wastewater in a low-cost, low-energy manner.
This document discusses strategies for Miami University to implement best management practices (BMPs) to improve stormwater management and earn LEED credits. It analyzes using vegetation buffers, rain gardens, green roofs, and rainwater cisterns. Recommendations include focusing BMPs in the South Patterson watershed and partnering with the Oxford community. Monitoring water quality at outfalls is suggested to show improvements and support credit applications.
Watersheds are important for several reasons. Unhealthy watersheds can negatively impact drinking water quality and cause problems like pesticides in wells. Current stormwater practices, streams buffers, and source controls have limited ability to reduce bacteria and other pollutants enough to meet water quality standards in most urban areas. Better watershed management is needed to prevent such problems.
Urban Stormwater Conditions and the Multiple Benefits of Green Infrastructure...RI_FMA
This document discusses urban stormwater issues in Providence, Rhode Island and the benefits of green infrastructure solutions. Providence faces challenges from aging infrastructure, high percentages of impervious surfaces, and industrial contamination near waterways. Green infrastructure approaches like rain gardens, swales, green roofs, and depaving lots can help address stormwater while providing community benefits like recreation, health, habitat, and economic development. Providence is pursuing green infrastructure projects in parks and vacant lots to manage stormwater and provide multiple benefits. Challenges remain around long-term maintenance of green infrastructure sites and further incentivizing private property owners.
This document provides an introduction to eight tools for watershed protection, summarizing each tool. The first tool discussed is land use planning, outlining how to develop a land use plan to meet water resource goals. Land use planning techniques like zoning are described. The second tool is land conservation, identifying five types of areas to conserve like critical habitats. Land conservation techniques are listed. The third tool discussed is establishing buffers along aquatic corridors, outlining their benefits and management considerations. The fourth tool is better site design to reduce impervious surfaces in developments. Key choices for applying each tool in a watershed are identified.
The Green Infrastructure Center helps communities implement green infrastructure solutions to manage stormwater and conserve natural areas. They provide guidance and case studies on using approaches like low impact development, green roofs, rain gardens, and trees to absorb and filter stormwater runoff. Overdevelopment has increased impervious surfaces and the amount of runoff, while reducing natural infrastructure like forests that previously absorbed water. The document discusses the benefits of green infrastructure in reducing flooding and pollution from stormwater while beautifying areas. It provides best practices for retrofitting existing development and incorporating green approaches into new projects.
The document discusses Peoria, Illinois' stream buffer ordinance. It defines a stream buffer as a protective, forested strip of land along both sides of a stream. Benefits of stream buffers include erosion control, flood management, water quality protection, and aesthetic and recreational value. Peoria developed its ordinance due to problems like unstable slopes and floodplain encroachment. The ordinance requires a 30-50 foot vegetated buffer on each side of streams and includes the 100-year floodplain. It allows for traditional compliance with buffer zones or alternative compliance through other conservation methods. The ordinance has led to reforestation of buffer areas and enforcement through fines for violations.
Water Resource Engineering - reportingVillyLagpao1
This document discusses water resource engineering. It covers topics like hydraulics for rivers, hydrology for rivers, and maritime hydraulics. Water resource engineering involves supplying water for human use and developing techniques to prevent flooding and remove excess water. Example projects discussed include farm irrigation systems, water treatment plants, wastewater treatment plants, and drainage systems. The document emphasizes that water resource engineering ensures a continuous supply of clean water for drinking and living through the design, construction, and maintenance of water management systems.
Sustainable urban drainage systems (SUDS) provide a natural approach to managing drainage around developments. SUDS slow and hold back rainwater and runoff from impervious surfaces like roads and buildings. This allows the water to be purified as it is held in wetland environments on site. The purified water is then slowly released into local waterways to prevent contamination. SUDS also increase biodiversity by creating habitats like ponds and wetlands that attract various wildlife.
Green infrastructure refers to using natural and engineered systems like vegetation and soils to manage stormwater. It provides stormwater control as well as social, economic, and environmental benefits. Some common types of green infrastructure include green roofs, rain gardens, porous pavements, vegetated swales, pocket wetlands, planter boxes, green parking lots, rain barrels, and downspout disconnection systems. Trees and forests are also important parts of green infrastructure that help filter water and reduce runoff.
This document provides information on constructed wetlands, which are shallow depressions that receive stormwater inputs for water quality treatment. They are typically less than 1 foot deep and have variable microtopography to promote dense wetland cover. Constructed wetlands are designed to achieve different levels of pollutant removal based on factors like plant community, hydrology source, and landscape position. They can reduce pollutants like phosphorus and nitrogen from stormwater and help control water flow. The document outlines design criteria for constructed wetlands including sizing, geometry, vegetation, and other considerations.
The document provides an overview of water resources management and hydrology. It discusses the goals of understanding hydrologic processes and solving water-related problems. Key topics covered include the water cycle, what hydrologists study and do, examples of ancient hydrologic history like the Nile River, major global water usage, water scarcity issues, and the shrinking of the Aral Sea as an example of poor water management.
Watershed management aims to conserve soil and water resources through various treatment measures. Deterioration of watersheds occurs due to faulty agriculture, forestry, mining and other human activities, resulting in less production, increased erosion, and lowered water tables. Watershed development components include soil management, water management, afforestation, and other interdependent activities. Measures for watershed treatment include contour trenches, bench terracing, check dams, plantation, and other methods suitable for agricultural land and hill slopes. The overall goal is to develop watersheds in a sustainable manner.
Enhancing Rainwater Harvesting through Pervious Pavement System Based on the ...civejjour
Pervious pavements are widely used in stormwater management practices due to their porosity.
However, the longevity and infiltration capacity could be greatly reduced with time due to
clogging issues. DakeRechsand manufactures pervious bricks from desert sand based on
principle of surface-free energy treatment. The pavers are made from desert sand that can
withstand against temperatures as high as 100 degrees Celsius and also handling freeze-thaw
cycle testing. This product range contains silica as the base material, has good anti-slippery
performance when wet. And observations showed that the there is less chance of black ice
formation on the brick surface, due to air-permeable propertities of the material. The company
has completed hundreds of projects mainly in China. Utilizing breathable desert sand using the
surface free energy is something not mastered before and DakeRechsand introduces an ecofriendly, sediment-free, recyclable, and much efficient technology to enhance rainwater
harvesting and water conservation.
Enhancing Rainwater Harvesting through Pervious Pavement System Based on the ...civejjour
Pervious pavements are widely used in stormwater management practices due to their porosity.
However, the longevity and infiltration capacity could be greatly reduced with time due to
clogging issues. DakeRechsand manufactures pervious bricks from desert sand based on
principle of surface-free energy treatment. The pavers are made from desert sand that can
withstand against temperatures as high as 100 degrees Celsius and also handling freeze-thaw
cycle testing. This product range contains silica as the base material, has good anti-slippery
performance when wet. And observations showed that the there is less chance of black ice
formation on the brick surface, due to air-permeable propertities of the material. The company
has completed hundreds of projects mainly in China. Utilizing breathable desert sand using the
surface free energy is something not mastered before and DakeRechsand introduces an ecofriendly, sediment-free, recyclable, and much efficient technology to enhance rainwater
harvesting and water conservation.
NY: A Green Infrastructure Approach - Onondaga Creek Water QualitySotirakou964
This document summarizes a report on improving water quality in Onondaga Creek through green infrastructure approaches. It provides background on combined sewer overflows polluting the creek and discusses planning efforts to reduce stormwater runoff volumes. The report selects a site for modeling green infrastructure techniques, including bioswales, curb cuts, rain gardens, blue roofs, and permeable surfaces. It analyzes costs and recommends the designed approaches as sustainable and cost-effective alternatives to traditional sewer infrastructure expansion.
Water resources engineering is concerned with controlling water quantity, quality, timing and distribution to meet human and environmental needs. It includes the disciplines of hydrodynamics, hydraulics, and hydrology. Water resources include surface water, groundwater, oceans, rivers, lakes, glaciers and snowfields. Water circulates through the hydrologic cycle of precipitation, runoff, storage, and evapotranspiration. Water resources development through engineering intervention is needed to meet uneven human demand, but must be done sustainably to ensure future generations' access to water without compromising environmental quality.
The document discusses changing stormwater regulations in Connecticut. Municipalities are increasingly requiring low impact development (LID) techniques to reduce stormwater pollution from development. LID aims to reduce impervious surfaces and runoff volumes to lower pollutant loads through techniques like bioretention basins, narrower roads, and permeable pavement. The document provides examples of LID projects and maintenance best practices to meet water quality goals and comply with new regulations.
This document provides information on sustainable stormwater management. It begins with an introduction on stormwater and the need for management. Examples of stormwater management techniques are then presented, including rain gardens, bioretention areas, vegetated swales, green roofs, and porous pavement. The installation processes for rain gardens and bioretention areas are described in multiple steps. Advantages and disadvantages of stormwater management are listed. The document concludes with references and appendices.
Watershed Managment by Muhammad Qasim & Aroj BashirMuhammad Qasim
This document discusses watershed management and its importance. It defines a watershed as an area where all water flows to a common outlet. It describes the key features of watersheds including size, terrain, soil type, and drainage divides. It outlines how human activities like pollution, overpopulation, and deforestation impact watersheds. The document advocates for watershed management to regulate pollution and monitor watershed health. It provides an example of a project improving sub-watershed management and environmental awareness in Pakistan's Ayubia National Park to contribute to sustainable water flows.
Gray vs. Green: The Role of Watershed-scale Green Infrastructure Systems for ...Mcrpc Staff
This document discusses the role of green infrastructure systems for managing wastewater at a watershed scale. It begins by outlining the historical patterns of water movement through uplands and lowlands, and how contemporary development has reversed these patterns. It then describes various green infrastructure strategies that can replicate natural hydrology, including green roofs, porous pavements, bio-retention systems, rainwater harvesting, wastewater recycling, and native landscaping. The document provides examples of these strategies and concludes by discussing a new paradigm in wastewater treatment using lagoons and floating mats of bacteria to polish wastewater in a low-cost, low-energy manner.
This document discusses strategies for Miami University to implement best management practices (BMPs) to improve stormwater management and earn LEED credits. It analyzes using vegetation buffers, rain gardens, green roofs, and rainwater cisterns. Recommendations include focusing BMPs in the South Patterson watershed and partnering with the Oxford community. Monitoring water quality at outfalls is suggested to show improvements and support credit applications.
Watersheds are important for several reasons. Unhealthy watersheds can negatively impact drinking water quality and cause problems like pesticides in wells. Current stormwater practices, streams buffers, and source controls have limited ability to reduce bacteria and other pollutants enough to meet water quality standards in most urban areas. Better watershed management is needed to prevent such problems.
Urban Stormwater Conditions and the Multiple Benefits of Green Infrastructure...RI_FMA
This document discusses urban stormwater issues in Providence, Rhode Island and the benefits of green infrastructure solutions. Providence faces challenges from aging infrastructure, high percentages of impervious surfaces, and industrial contamination near waterways. Green infrastructure approaches like rain gardens, swales, green roofs, and depaving lots can help address stormwater while providing community benefits like recreation, health, habitat, and economic development. Providence is pursuing green infrastructure projects in parks and vacant lots to manage stormwater and provide multiple benefits. Challenges remain around long-term maintenance of green infrastructure sites and further incentivizing private property owners.
This document provides an introduction to eight tools for watershed protection, summarizing each tool. The first tool discussed is land use planning, outlining how to develop a land use plan to meet water resource goals. Land use planning techniques like zoning are described. The second tool is land conservation, identifying five types of areas to conserve like critical habitats. Land conservation techniques are listed. The third tool discussed is establishing buffers along aquatic corridors, outlining their benefits and management considerations. The fourth tool is better site design to reduce impervious surfaces in developments. Key choices for applying each tool in a watershed are identified.
The Green Infrastructure Center helps communities implement green infrastructure solutions to manage stormwater and conserve natural areas. They provide guidance and case studies on using approaches like low impact development, green roofs, rain gardens, and trees to absorb and filter stormwater runoff. Overdevelopment has increased impervious surfaces and the amount of runoff, while reducing natural infrastructure like forests that previously absorbed water. The document discusses the benefits of green infrastructure in reducing flooding and pollution from stormwater while beautifying areas. It provides best practices for retrofitting existing development and incorporating green approaches into new projects.
The document discusses Peoria, Illinois' stream buffer ordinance. It defines a stream buffer as a protective, forested strip of land along both sides of a stream. Benefits of stream buffers include erosion control, flood management, water quality protection, and aesthetic and recreational value. Peoria developed its ordinance due to problems like unstable slopes and floodplain encroachment. The ordinance requires a 30-50 foot vegetated buffer on each side of streams and includes the 100-year floodplain. It allows for traditional compliance with buffer zones or alternative compliance through other conservation methods. The ordinance has led to reforestation of buffer areas and enforcement through fines for violations.
Water Resource Engineering - reportingVillyLagpao1
This document discusses water resource engineering. It covers topics like hydraulics for rivers, hydrology for rivers, and maritime hydraulics. Water resource engineering involves supplying water for human use and developing techniques to prevent flooding and remove excess water. Example projects discussed include farm irrigation systems, water treatment plants, wastewater treatment plants, and drainage systems. The document emphasizes that water resource engineering ensures a continuous supply of clean water for drinking and living through the design, construction, and maintenance of water management systems.
Sustainable urban drainage systems (SUDS) provide a natural approach to managing drainage around developments. SUDS slow and hold back rainwater and runoff from impervious surfaces like roads and buildings. This allows the water to be purified as it is held in wetland environments on site. The purified water is then slowly released into local waterways to prevent contamination. SUDS also increase biodiversity by creating habitats like ponds and wetlands that attract various wildlife.
Green infrastructure refers to using natural and engineered systems like vegetation and soils to manage stormwater. It provides stormwater control as well as social, economic, and environmental benefits. Some common types of green infrastructure include green roofs, rain gardens, porous pavements, vegetated swales, pocket wetlands, planter boxes, green parking lots, rain barrels, and downspout disconnection systems. Trees and forests are also important parts of green infrastructure that help filter water and reduce runoff.
This document provides information on constructed wetlands, which are shallow depressions that receive stormwater inputs for water quality treatment. They are typically less than 1 foot deep and have variable microtopography to promote dense wetland cover. Constructed wetlands are designed to achieve different levels of pollutant removal based on factors like plant community, hydrology source, and landscape position. They can reduce pollutants like phosphorus and nitrogen from stormwater and help control water flow. The document outlines design criteria for constructed wetlands including sizing, geometry, vegetation, and other considerations.
The document provides an overview of water resources management and hydrology. It discusses the goals of understanding hydrologic processes and solving water-related problems. Key topics covered include the water cycle, what hydrologists study and do, examples of ancient hydrologic history like the Nile River, major global water usage, water scarcity issues, and the shrinking of the Aral Sea as an example of poor water management.
Watershed management aims to conserve soil and water resources through various treatment measures. Deterioration of watersheds occurs due to faulty agriculture, forestry, mining and other human activities, resulting in less production, increased erosion, and lowered water tables. Watershed development components include soil management, water management, afforestation, and other interdependent activities. Measures for watershed treatment include contour trenches, bench terracing, check dams, plantation, and other methods suitable for agricultural land and hill slopes. The overall goal is to develop watersheds in a sustainable manner.
Enhancing Rainwater Harvesting through Pervious Pavement System Based on the ...civejjour
Pervious pavements are widely used in stormwater management practices due to their porosity.
However, the longevity and infiltration capacity could be greatly reduced with time due to
clogging issues. DakeRechsand manufactures pervious bricks from desert sand based on
principle of surface-free energy treatment. The pavers are made from desert sand that can
withstand against temperatures as high as 100 degrees Celsius and also handling freeze-thaw
cycle testing. This product range contains silica as the base material, has good anti-slippery
performance when wet. And observations showed that the there is less chance of black ice
formation on the brick surface, due to air-permeable propertities of the material. The company
has completed hundreds of projects mainly in China. Utilizing breathable desert sand using the
surface free energy is something not mastered before and DakeRechsand introduces an ecofriendly, sediment-free, recyclable, and much efficient technology to enhance rainwater
harvesting and water conservation.
Enhancing Rainwater Harvesting through Pervious Pavement System Based on the ...civejjour
Pervious pavements are widely used in stormwater management practices due to their porosity.
However, the longevity and infiltration capacity could be greatly reduced with time due to
clogging issues. DakeRechsand manufactures pervious bricks from desert sand based on
principle of surface-free energy treatment. The pavers are made from desert sand that can
withstand against temperatures as high as 100 degrees Celsius and also handling freeze-thaw
cycle testing. This product range contains silica as the base material, has good anti-slippery
performance when wet. And observations showed that the there is less chance of black ice
formation on the brick surface, due to air-permeable propertities of the material. The company
has completed hundreds of projects mainly in China. Utilizing breathable desert sand using the
surface free energy is something not mastered before and DakeRechsand introduces an ecofriendly, sediment-free, recyclable, and much efficient technology to enhance rainwater
harvesting and water conservation.
The document discusses the challenges of achieving Code for Sustainable Homes Level 6 certification for new home construction in the UK. Level 6 is the highest level under the code and requires obtaining the maximum number of credits across nine categories related to energy/CO2 emissions, water, materials, surface water runoff, waste, pollution, health and well-being, management, and ecology. While some local planning departments may require Level 6, achieving it would be difficult and costly. Homes would need to be nearly zero-energy, have highly efficient fittings and appliances, minimize waste and promote ecology/biodiversity on site.
Managing stormwater runoff is challenging for urban areas due to increasing amounts of impermeable surfaces like roads and sidewalks. This causes problems like flooding and reduced water quality. Permeable pavement is an effective strategy for stormwater management that allows water to infiltrate instead of running off. It comes in forms like pervious concrete, porous asphalt, and interlocking pavers. Permeable pavement provides environmental benefits such as reduced flooding, increased groundwater recharge, and improved water quality by filtering pollutants from runoff.
This document discusses efficient use of rain water by altering road drainage systems. It describes how stagnant rain water on roads can degrade surfaces and cause potholes. The document proposes collecting stagnant water and modernizing drainage systems. It explains how altering road slopes and materials used can help drain water more effectively and recharge groundwater tables. The document also discusses drainage system types, how potholes form, methods for repairing potholes, and the importance of proper road slopes for drainage.
Efficient Use of Rain Water by Altering Channel Systemtheijes
The International Journal of Engineering & Science is aimed at providing a platform for researchers, engineers, scientists, or educators to publish their original research results, to exchange new ideas, to disseminate information in innovative designs, engineering experiences and technological skills. It is also the Journal's objective to promote engineering and technology education. All papers submitted to the Journal will be blind peer-reviewed. Only original articles will be published.
This document summarizes a research paper that proposes an efficient way to collect and use storm water runoff from roads by altering the channel system beneath the road surface. The system involves digging channels underneath the road, lining them with cement, and covering them with perforated stones to allow water to flow through while still supporting vehicle loads. This would prevent water stagnation on roads, reduce pothole formation, and help meet water demands, while only requiring higher initial construction costs. Collecting storm water in this way could have benefits like lessening water scarcity, improving traffic flow, and controlling diseases spread by standing water.
Our biggest challenge in this new century is to take an idea that seems abstract – sustainable development – and turn it into a reality for all the world’s people. Rampant urbanization and climate changes have triggered severe and frequent natural disasters. Green infrastructure provides an opportunity to reassess how we manage and use green spaces through the identification and provision of interconnected green spaces that protect, manage and enhance environmental resources. Successful green and blue infrastructure planning is recognized as a natural solution and less expensive alternative to conventional 'grey' infrastructure that is environmentally friendly. As we are at the edge of climate change tipping points, integrating blue-green-grey infrastructure is a necessity to design sustainable and climate resilient cities.
1. Current irrigation techniques like surface irrigation have low efficiencies of around 40% due to evaporation, deep percolation, and management losses. Subsurface irrigation is more efficient but also more expensive.
2. The paper proposes combining subsurface irrigation using permeable pipes with an ancient technique of pot irrigation to provide auto-regulation. Permeable pipes would have advantages of mechanized installation and scale while pot irrigation provides low-cost auto-regulation without external control.
3. Current material investigations are exploring polymer fibers with a mineral layer on a pipe shell or a non-woven membrane layer to provide appropriate hydraulic conductivity and permeability for the auto-regulative permeable pipes. Locally available materials will also be
IRJET- Exprimental Analysis of Permeable Concrete and its Application over Co...IRJET Journal
Permeable concrete is an alternative pavement method that allows stormwater to infiltrate through the surface into underlying layers, reducing runoff. It can be used for applications like driveways, parking lots, and low traffic roads. The paper discusses the benefits of permeable concrete in reducing runoff and filtering pollutants from water. It also notes future research opportunities to expand its uses and improve the longevity and cost-effectiveness of permeable concrete systems.
Group 5 sustainable stormwater management(building services1)kohwenqi
This document provides information on sustainable stormwater management. It begins with an introduction on stormwater and the need for management. Examples of stormwater management techniques are then presented, including rain gardens, bioretention areas, vegetated swales, green roofs, and porous pavement. The installation processes for rain gardens and bioretention areas are described in multiple steps. Advantages and disadvantages of stormwater management are listed. The document concludes with references and appendices.
IRJET- Review of Stormwater Management using Pervious Concrete in PavementsIRJET Journal
This document summarizes the use of pervious concrete in pavements for stormwater management. Pervious concrete is a porous pavement that allows water to seep through it and infiltrate into the soil below. It has high void percentages compared to ordinary concrete, allowing flow rates of 2-18 gallons per minute. Pervious concrete provides environmental benefits like eliminating runoff, recharging groundwater, and trapping pollutants. It also has financial benefits such as reducing costs for stormwater infrastructure and de-icing. The document discusses mix designs used for pervious concrete and its layers, which include concrete, aggregates, geotextiles, and paver blocks or soil on top. Pervious concrete is a durable product that can
This document provides an overview of pervious concrete, including its composition, benefits for stormwater management, and design considerations. Pervious concrete is a special type of concrete with a high porosity that allows water to pass through it. This helps recharge groundwater and reduce stormwater runoff compared to traditional impervious concrete. The document discusses the materials used to make pervious concrete, including cement, coarse aggregates, and little to no fine aggregates. It also reviews different paving materials like asphalt, concrete, brick, stone, tile, wood, and earth materials; and notes factors like durability, porosity, installation and maintenance costs for each.
This document provides an overview of pervious concrete, including its environmental benefits, applications, performance characteristics, construction procedures, and testing methods. Key points include:
- Pervious concrete allows rainwater to seep through it, reducing runoff and recharging groundwater while meeting EPA stormwater regulations.
- It has sufficient strength for many pavement applications despite its high porosity (15-25% voids) and permeability rates of 480 in/hr or more.
- Applications include pavements for parking lots where it can eliminate the need for retention ponds and swales by capturing and filtering rainwater.
- Proper construction techniques like vibration and curing are important for performance. Visual inspections, infiltration tests
This document is prepared for our major project submission for B.tech degree. the project deals with improvement of compressive strength of pervious concrete with out affecting its permeability property much.
Rainwater harvesting is an important traditional practice in India that has declined with urbanization. It is needed now more than ever to address water shortages and declining groundwater levels. Roof rainwater harvesting systems collect rainwater and store it for use or allow it to percolate to recharge groundwater. Proper filtration is important to ensure water quality. Traditional methods like step wells and tanks helped conserve water and communities were responsible for maintenance. Reviving such systems with public participation can help address the water crisis through a decentralized approach.
SCHOTT Solar manufactures polycrystalline solar modules that offer industry-leading 25-year linear power output warranties and are tested to stringent reliability standards; the modules are produced in Germany and also at SCHOTT Solar's US facility in Albuquerque, New Mexico, where they qualify as domestic products under various US acts.
The parking lot design consists of asphalt in driveway areas and porous pavers in parking stalls and pedestrian areas. The porous pavers aid stormwater runoff design and aesthetics. Five electric vehicle parking stalls with outlets and bike racks will promote sustainability. Four handicapped spaces meet ADA guidelines, and the porous pavers improve accessibility. The lot slopes to drain stormwater through pipes under the lot to the storm sewer. The total cost is $346,753, with $172,194 for asphalt driveways and $174,559 for porous paver parking stalls.
Geotech and pavement design informationcathexis123
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1. Improving Storm Water Management
Situation / Impervious surfaces’negative effects / Challenges for city officials
Sustainable development is meeting the needs of the present without compromising the
ability of future generations to meet their own needs. (Our common future, 1987, World
Commission on Environment and Development. Oxford, UK. Oxford University Press).
As the need for sustainable development increases, city officials are faced with the
challenge of rehabilitating municipal infrastructures to ensure a better use of nature’s
resources and minimize the impact of human activity on our environment, while still
promoting the development of North America’ urban landscapes.
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Previous urban sprawl over the continent as happened with little regards for the
environment, nor towards the potential further development of growing cities. The
proliferation of impervious surfaces over the land and the conveyance of rain water via
urban infrastructure have had grave consequences over the natural hydrological cycle.
A study by the US EPA (Urbanization and Streams: Studies of Hydrologic Impacts)
shows that increased imperviousness leads to:
? ? increased flow volumes, peaks and peak durations
? ? increased stream temperature
? ? changes in sediment loading
? ? reduction of infiltration to aquifers
? ? entrainment of pollutants to receiving waters
The rising impermeability of surfaces has limited the recharging of soil water reserves,
thus drying out the soils from which plant roots draw their nutrients. Dry soils also
become more prone to erosion.
Unable to leech down through the surface, rain water gathers sediments and ground
pollutants as they dramatically increase surface runoffs through urban infrastructure,
flowing down to receiving waters.
This has affected humans at the expense of the environment around which we live, as
well as economically, raising costs of development and maintenance of infrastructures.
Economics
Citizens the world over are now more than ever aware of the financial costs of poor
environmental planning. The increasing presence of impervious surfaces proves very
costly, as government authorities must spend more to build larger sewer infrastructures to
carry increasing flows.
2. Land developers are also losing money. Wishing to connect the sewers of new
developments to existing pipes already functioning at capacity, retention ponds must be
built on land, which would otherwise be sold to residential owners.
The combination of increased flow rates and drying of the soil has dramatically amplified
erosion of streams and embankments of receiving water bodies. And while very onerous
engineered methods are implanted to counter erosion, the true cost of soil deterioration is
still unknown.
Poor water quality is also proving very costly. Polluted waters reaching main water
bodies degrade the natural habitat, adversely affecting industries such as tourism and
fisheries. The decontamination of overflows is also very expensive as the activities at
sewer treatment plants augment.
Realizing the impact of today’ actions on the world of tomorrow, elected officials,
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municipal engineers, architects and urban planners are now more than ever concentrating
their efforts on finding solutions that are economically and environmentally viable for the
next generations.
Best Management Practices
To improve sustainable development, U.S. federal law now requires, through the
National Pollution Discharge Elimination System (NPDES), that states control non-point
source water pollution. Best Management Practices are techniques identified by state
authorities to achieve this goal. Regional laws include limitations on the percentage of
impervious surface over a total development, restrictions on outflow volume and velocity
to the existing infrastructures, outflow contaminant concentrations, and others.
Adopting a BMP is not only encouraged through legislation, but provides promoters,
authorities and residents with a great tool to enhance their comfort while ensuring great
medium and long term return on investment.
Objectives
When choosing a BMP, administrators should consider a wide range of factors. The right
solution will answer the immediate environmental needs, through a long life-cycle, at a
reasonable price. The right solution must also answer the most issues, as the owner
wishes to limit the variety of techniques implemented.
Permeable Pavement
Permeable pavements are one of the most popular and appreciated BMPs. They answer
both qualitative and quantitative needs for precipitation water flows. As water rains on
the pavement, it seeps through to the ground, reducing surface flows, often even
eliminating the need for sewers and manholes.
3. The key to understanding permeable pavements is to perceive the pavement and the base
aggregates as a system, instead of separate products. As water rains down on the
pavement, it begins its journey by seeping through the pavement, and then through the
base aggregates, which naturally filter the pollutants. As it travels down, the water is
stored in the base, until it reaches the natural underlying soils and recharges the ground
aquifers. Thus, permeable pavement serves as an underground storage basin that filters
the water while allowing pedestrian and vehicular traffic on the surface.
Depending on site conditions and owner preferences, permeable pavement can be
designed to obtain full, partial or zero exfiltration (figures 1 a,b,c). Full exfiltration is the
most often desired and used application, which sees all the rain water stored in the base
leeching down to the underlying subgrade. When natural soils are not permeable enough,
or storms too heavy, perforated pipes are added to alleviate the excess water. Thirdly, an
impermeable geo-membrane can be installed above the natural soils to prevent
exfiltration of contaminated flows when the pavement is installed in industrial sites.
4. Impermeable
membrane
Figure 1 a) Full exfiltration to subgrade (Oldcastle, 2008). b) Partial
exfiltration to subgrade (ICPI, 2006). c) No exfiltration to subgrade (Oldcastle, 2008)
5. Choosing permeable pavement technology, the designer or owner will benefit from
(ICPI, 2006):
? ? Conservation of space on the site and reduction of impervious cover
? ? Reduction of runoff
o Reduced peak discharge and stress on sewers
o Reduction of downstream erosion
? ? Improved water quality
? ? Reduction of water temperature
? ? Increased recharge of groundwater
o Promote tree survival by providing air and water to the roots
? ? Reduction of total development costs
o Reduction of infrastructure construction
o Decrease in retention basins and other unsellable land
? ? Reduces risks of accidents/injuries
o Eliminates puddling and flooding on parking lots
o Faster snow melt drainage
? ? Contributes to urban heat island reduction
? ? Eligible for LEED® credits
LEED® Credits
As detailed on ICPI’ Tech Spec 16, more than 13 LEED points can be obtained, directly
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or indirectly, through the use of permeable pavements.
The most obvious credits attainable through the use of permeable pavements are
Sustainable Sites 6.1 and Sustainable Sites 6.2, covering imperviousness and pollutant
filtration respectively.
Also, through the right choice of permeable pavements, points can be attributed for
reduction of heat island effect, reused or recycled materials, regional materials, pavement
lifecycle, water efficiency and utility durability plans.
Permeability and Beyond
Though the main use of permeable pavements is reduction of storm water flows, it can
sure be the main entryway for other technologies, mainly water harvesting. While the
infiltrated water isn’ quite potable for consumption, it can be stored for a wide array of
t
uses, ranging from
? ? landscape irrigation
? ? root system maintenance
? ? building graywater applications (flushes, and such)
6. Figure 1
Permeable Interlocking Concrete Pavement
To answer the growing needs of the emerging permeable pavement market,
manufacturers have brought forth products that can be separated in two major categories:
? ? interlocking units that let the water seep through pervious material filling the
joints and openings
? ? porous material that lets the water seep through itself
Permeable interlocking concrete pavements, PICP, consist of separate paver units, laid
down on a surface in a particular pattern, separated by narrow joints and shaped holes,
both filled with pervious aggregates. Porous material, whether it is asphalt or concrete,
presents a sponge-like matrix. Water flows through the PICP’ aggregate-filled joints, or
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directly through the porous material.
While both have their merits, interlocking units are often preferred for their:
? ? better aesthetics (wide range of shapes, colors, textures)
? ? ease of replacement, rehabilitation
? ? ease of maintenance
Holes and cavity are rampant all over the face of porous concrete or asphalt, strongly
limiting the textures that can be applied to the visible surface. However, PICP unit
pavers can be textured the same way regular pavers are, giving the pavement any look the
designer desires.
Also, when the pavement undergoes damage, PICP is easier to repair as the separate units
can easily be lifted off and replaced. Meanwhile, asphalt and poured concrete, require
that the pavement be sawed and that excavators be used to lift the material. Not to worry,
the pavers are vandalism proof as special clamps are required to remove the pavers from
the pavement.
Finally, porous concrete’ matrix like structure makes it difficult to vacuum sediments
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clogged inside the pores. The maintenance of PICP consists simply of vacuuming the
7. superficial layer of aggregates and replenishing the joints. The vacuumed aggregates can
then be cleaned and reused; some vacuum equipment can be controlled to remove
sediment particles while minimizing removal of the aggregate.
Design
A proper permeable pavement will be designed according to regional factors and
environment. While general guidelines are provided, a local engineer should always
confirm the design to suit the client’ needs.
s
Based on site specific geological surveys, local hydrological collected data and
predictions, as well as the owner’ design purposes, the engineer will prepare and
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approve plans that are best suited for the particular project. Figure 3 presents the general
variables that must be accounted for through the design of the permeable interlocking
concrete pavement system.
Figure 3 Figure is property of ICPI. May be used with permission only.
Sustainable urban development requires that the infrastructure be designed for a longer
life-cycle. The life expectancy of a PICP system depends on the proper maintenance of
the pavement. As time goes by, sediments from all sources will deposit over the draining
8. aggregates, clogging the pores and reducing the system’ efficiency. To preserve the
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optimal drainage qualities of the pavement, the owner should implement a maintenance
program, vacuuming debris once or twice a year.
Studies performed by the Interlocking Concrete Pavement Institute have shown that a
non-maintained system’ permeability could decrease by 90% of its original design value
s
(figure 4). While continued maintenance of the system would prevent such dramatic
reduction in the infiltration rate, the designing engineer should prepare for the worst case
scenario. To avoid system failure, it is recommended that the engineer design the
pavement to still function after an 80 to 90% decrease in permeability.
Figure 4 Overall trend of infiltration performance (Borgwardt, 2006) To be used with
permission only.
Installation
The most common cause of failure in permeable pavements is faulty installation. It is
crucial for the best functioning of the pavement that care be taken during installation to
avoid fine particle contamination of the open-graded aggregate base. To maximize
system efficiency and customer satisfaction, the Interlocking Concrete Pavement Institute
offers PICP training as part of its Level II Paver Contractor Certification. It is
recommended that clients seek out accredited professionals. Pavement installation
guidelines are attached in Annex 1.
Subterra Permeable Pavement
Definition
The Subterra is the industry’ best looking permeable paver, combining Oldcastle’s
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renowned textures and colors with all the technical characteristics necessary to ensure an
efficient environmentally-friendly pervious surface. Subterra was created to answer the
9. sustainable development needs of eco-aware residential owners/promoters and
municipalities eager to bestow a premier look to their pedestrian and low-traffic areas.
Shape
Subterra® consists of twelve (12) different stones. While each stone has a constant
rectangular shape, easing installation, false joints run along the stone’ surface, giving it a
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unique randomly set, modular look of natural cobble stone, which is easily enhanced
through three possible laying patterns.
Figure 5 Herringbone, stacked and offset laying patterns
Subterra’ patented hole at the cross-section of the false joints in the middle of the paver
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also increases the open-ratio without comprising the aesthetics of the landscaped area.
Texture
Beyond shape, Subterra also seduces homeowners with its bush-hammered texture,
bringing Subterra a full generation ahead of the other permeable pavers on the market.
Up to six different natural looking face textures are available.
Technical data
Permeability
Like most natural processes the environmental efficiency of a PICP system marvels by its
simplicity. The permeability is determined by the amount of water that infiltrates through
the surface in a given period of time, also referred to as the flow rate. Mathematically, it
is the speed at which water travels through the pervious media, multiplied by the area of
the surface, which is filled by the aggregates.
The speed at which water travels through the aggregate is a characteristic property of the
aggregate itself. The more pores between the aggregates, the faster the water travels.
The quality of the aggregate is therefore determined, in part, by the gradation of the
sieved material, which must contain the least proportion of fines as possible (see
installation guideline).
10. Figure 6
Of course, any paver can be installed with wide joints. Combining elegance with
functionality, Subterra as been designed so as to optimize the joint widths without
sacrificing the hardscaped architecture. The combination of joint and hole open-space on
a Subterra pavement averages a 6.8% opening ratio.
To determine the amount of water percolating through the surface, the hydraulic
conductivity is thus, multiplied by the area of the opening.
A recurrent error in the design of permeable pavements is the use of a brand new
system’ infiltration rate as a basis for design. American and German experience
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recommend that a conservative design rate of 10% of the initial rate be used to take into
account clogging over a 20 year period (Interpave, www.paving.org.uk). To help
engineers plan storm water structures, an independent firm has tested a brand new
Subterra stone’ infiltration, which has then been reduced for a conservative estimate of
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90% clogging.
Freeze and Thaw
In colder climates, pavements are often in poor condition as the expanded ice melts and
surfaces crumble. Fortunately, the pores between the open-graded aggregates are enough
as to allow the typical 10% expansion of frozen water, thus safeguarding the permeable
pavement from the heaving motion. The reduction in potholes provides more secure
surfaces for the public and cheaper maintenance for the owner.
11. Dimensions
Figure 7 Subterra Board Layout
A board layout of Subterra stone comes with twenty stones, each unique in its
combination of textures and false joints, guaranteeing a truly random cobble stone look.
Though the finished appearance seems to gather pieces of different size, every stone is
actually rectangular in shape (80 mm high X 276 mm long X 180 mm wide), thus easing
installation.
ADA Compliancy
The American Disabilities Act requires that safe and easy to travel paths be available to
guarantee access for people with reduced mobility. It is required that a surface be stable,
slip-free, and that difference in elevations and joint spacing do not surpass a quarter and
half of an inch, respectively. Mindful of the safety and comfort of all users, Subterra
stone textures and spacers (11 mm) have been designed to respect these criteria.
Case Study
Since its inception on the market, brand new Subterra stones have been highlighted
throughout the country, notably on the HGTV specialty show, Inside Out. As seen on
figure 2, the result is a classic look, sure to harmonize with most residential and
neighborhood architectures.
12. Figure 8 Subterra, installed on HGTV show Inside Out
ANNEX 1
DETAILED PAVEMENT INSTALLATION GUIDELINES
SECTION 32 14 13.19
PERMEABLE INTERLOCKING CONCRETE PAVEMENT
Note: This guide specification for Canadian applications describes construction of
permeable interlocking concrete pavers on a permeable, open-graded crushed stone
bedding layer (typically No. 8 stone). This layer is placed over an open-graded base
(typically No. 57 stone) and sub-base (typically No. 2 stone). The pavers and bedding layer
are placed over an open-graded crushed stone base with exfiltration to the soil subgrade. In
low infiltration soils or installations with impermeable liners, some or all drainage is directed
to an outlet via perforated drain pipes in the subbase. While this guide specification does
not cover excavation, liners and drain pipes, notes are provided on these aspects.
The text must be edited to suit specific project requirements. It should be reviewed by a
qualified civil or geotechnical engineer, or landscape architect familiar with the site
conditions. Edit this specification term as necessary to identify the design professional in the
General Conditions of the Contract.
PART 1 GENERAL
1.01 SUMMARY
A. Section Includes
13. 1. Permeable interlocking concrete pavers.
2. Crushed stone bedding material.
3. Open-graded subbase aggregate.
4. Open-graded base aggregate.
5. Bedding and joint/opening filler materials.
6. Edge restraints.
7. [Geotextiles].
B. Related Sections
1. Section [_______]: Curbs.
2. Section [_______]: [Stabilized] aggregate base.
3. Section [_______]: [PVC] Drainage pipes
4. Section [_______]: Impermeable liner.
5. Section [_______]: Edge restraints.
6. Section [_______]: Drainage pipes and appurtenances.
7. Section [_______]: Earthworks/excavation/soil compaction.
1.02 REFERENCES
A. American Society for Testing and Materials (ASTM)
1. C 67, Standard Test Methods for Sampling and Testing Concrete Masonry
Units and Related Units.
2. C 131, Standard Test Method for Resistance to Degradation of Small-Size
Coarse Aggregate by Abrasion and Impact in the Los Angeles Machine.
3. C 136, Method for Sieve Analysis for Fine and Coarse Aggregate.
4. C 140, Test Methods for Sampling and Testing Brick and Structural Clay Tile,
Section 8 – Freezing and Thawing.
5. D 448, Standard Classification for Sizes of Aggregate for Road and Bridge
Construction.
6. C 979, Specification for Pigments for Integrally Colored Concrete.
7. D 698, Test Methods for Moisture Density Relations of Soil and Soil Aggregate
Mixtures Using a 5.5-lb (2.49 kg) Rammer and 12 in. (305 mm) drop.
8. D 1557, Test Methods for Moisture Density Relations of Soil and Soil Aggregate
Mixtures Using a 10-lb (4.54 kg) Rammer and 18 in. (457 mm) drop.
9. D 1883, Test Method for California Bearing Ratio of Laboratory-Compacted
Soils.
10. D 4254, Standard Test Methods for Minimum Index Density and Unit Weight of
Soils and Calculation of Relative Density.
B. Canadian Standards Association (CSA)
1. A231.2 Precast Concrete Pavers
C. Interlocking Concrete Pavement Institute (ICPI)
1. Permeable Interlocking Concrete Pavement manual.
1.03 SUBMITTALS
A. In accordance with Conditions of the Contract and Division 1 Submittal Procedures
Section.
B. Manufacturer’ drawing and details: Indicate perimeter conditions, junction with other
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materials, expansion and control joints, paver [layout,] [patterns,] [color arrangement,]
installation [and setting] details. Indicate layout, pattern, and relationship of paving
joints to fixtures and project formed details.
C. Minimum 2 kg samples of subbase, base and bedding aggregate materials.
D. Sieve analysis of aggregates for subbase, base and bedding materials per ASTM C
136.
E. Soils report indicating density test reports, classification, and infiltration rate measured
on-site under compacted conditions, and suitability for the intended project.
F. Erosion and sediment control plan.
G. [Stormwater management (quality and quantity) calculations.]
H. Permeable concrete pavers:
14. 1. Manufacturer’ product catalog sheets with specifications.
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2. [Four] representative full-size samples of each paver type, thickness, color, and
finish. Submit samples indicating the range of color expected in the finished
installation.
3. Accepted samples become the standard of acceptance for the work of this
Section.
4. Laboratory test reports certifying compliance of the concrete pavers with ASTM
C 936.
5. Manufacturer’ material safety data sheets for the safe handling of the specified
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materials and products.
6. Manufacturer’ written quality control procedures including representative
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samples of production record keeping that ensure conformance of paving
products to the project specifications.
H. Paver Installation Subcontractor:
1. A copy of Subcontractor’ current certificate from the Interlocking Concrete
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Pavement Institute Concrete Paver Installer Certification program.
2. Job references from projects of a similar size and complexity. Provide
Owner/Client/General Contractor names, postal address, phone, fax, and email
address.
3. Written Method Statement and Quality Control Plan that describes material
staging and flow, paving direction and installation procedures, including
representative reporting forms that ensure conformance to the project
specifications.
1.04 QUALITY ASSURANCE
A. Paver Installation Subcontractor Qualifications:
1. Utilize an installer having successfully completed concrete paver installation
similar in design, material and extent indicated on this project.
2. Utilize an installer holding a current certificate from the Interlocking Concrete
Pavement Institute Concrete Paver Installer Certification program.
B. Regulatory Requirements and Approvals: [Specify applicable licensing, bonding or
other requirements of regulatory agencies.].
C. Review the manufacturers’quality control plan, paver installation subcontractor’ s
Method Statement and Quality Control Plan with pre-construction meeting of
representatives from the manufacturer, paver installation subcontractor, general
contractor, engineer and/or owner’ representative.
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C. Mock-Ups:
1. Install a 3 x 3 m paver area.
2. Use this area to determine surcharge of the bedding layer, joint sizes, lines,
laying pattern(s), color(s) and texture of the job.
3. This area will be used as the standard by which the work will be judged.
4. Subject to acceptance by owner, mock-up may be retained as part of finished
work.
5. If mock-up is not retained, remove and properly dispose of mock-up.
1.05 DELIVERY, STORAGE, AND HANDLING
A. General: Comply with Division 1 Product Requirement Section.
B. Comply with manufacturer’ ordering instructions and lead-time requirements to avoid
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construction delays.
C. Delivery: Deliver materials in manufacturer’ original, unopened, undamaged
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container packaging with identification tags intact on each paver bundle.
1. Coordinate delivery and paving schedule to minimize interference with normal
use of buildings adjacent to paving.
2. Deliver concrete pavers to the site in steel banded, plastic banded, or plastic
wrapped cubes capable of transfer by forklift or clamp lift.
3. Unload pavers at job site in such a manner that no damage occurs to the
15. product or existing construction
D Storage and Protection: Store materials in protected area such that they are kept free
from mud, dirt, and other foreign materials.
1.06 ENVIRONMENTAL REQUIREMENTS
A. Do not install in rain or snow.
B. Do not install frozen bedding materials.
1.07 MAINTENANCE
A. Extra materials: Provide [Specify area] [Specify percentage] additional material for
use by owner for maintenance and repair.
B. Pavers shall be from the same production run as installed materials.
PART 2 PRODUCTS
Note: Some projects may include permeable and solid interlocking concrete pavements. Specify
each product as required.
A. Manufacturer: Permacon
1. Contact: [Specify ICPI member manufacturer contact information.].
B. Permeable Interlocking Concrete Paver Units:
1. Paver Type: [Specify name of product group, family, series, etc.].
a. Material Standard: Comply with CSA A231,2.
b. Color [and finish]: [Specify color.] [Specify finish].
c. Color Pigment Material Standard: Comply with ASTM C 979.
Note: Concrete pavers may have spacer bars on each unit. Spacer bars are recommended
for mechanically installed pavers. Manually installed pavers may be installed with or without
spacer bars. Verify with manufacturers that overall dimensions do not include spacer bars.
d. Size: [Specify] mm x [Specify] mm x [Specify] mm thick.
2.02 PRODUCT SUBSTITUTIONS
A. Substitutions: No substitutions permitted.
2.03 CRUSHED STONE FILLER, BEDDING, BASE AND SUBBASE
A. Crushed stone with 90% fractured faces, LA Abrasion < 40 per ASTM C 131,
minimum CBR of 80% per ASTM D 1883.
B. Do not use rounded river gravel.
C. All stone materials shall be washed with less than 1% passing the 0.080 mm sieve.
D. Joint/opening filler, bedding, base and subbase: conforming to ASTM D 448 gradation
as shown in Tables 1, 2 and 3 below:
Note: No. 89 or finer gradation may be used to fill permeable pavers with narrow joints.
Table 1
ASTM No. 8 Grading Requirements
Bedding and Joint/Opening Filler
Sieve Size Percent Passing
12.5 mm 100
9.5 mm 85 to 100
4.75 mm 10 to 30
2.36 mm 0 to 10
1.16 mm 0 to 5
Table 2
16. ASTM No. 57 Base
Grading Requirements
Sieve Size Percent Passing
37.5 mm 100
25 mm 95 to 100
12.5 mm 25 to 60
4.75 mm 0 to 10
2.36 mm 0 to 5
Table 3
Grading Requirement for ASTM No. 2 Subbase
Sieve Size Percent Passing
75 mm 100
63 mm 90 to 100
50 mm 35 to 70
37.5 mm 0 to 15
19 mm 0 to 5
E. Gradation criteria for the bedding and base:
Note: Dx is the particle size at which x percent of the particles are finer. For example, D15 is
the particle size of the aggregate for which 15% of the particles are smaller and 85% are
larger.
1. D15 base stone /D50 bedding stone < 5.
2. D50 base stone/D50 bedding stone > 2.
2.04 ACCESSORIES
A. Provide accessory materials as follows:
Note: Curbs will typically be cast-in-place concrete or precast set in concrete haunches.
Concrete curbs may be specified in another Section. Do not use plastic edging with steel
spikes to restrain the paving units.
1. Edge Restraints
a. Manufacturer: [Specify manufacturer.].
b. Material: [Pre-cast concrete] [Cut stone] [Concrete].
b. Material Standard: [Specify material standard.].
Note: See ICPI publication, Permeable Interlocking Concrete Pavements for guidance on
geotextile selection. Geotextile use is optional.
2. Geotextile Fabric:
a. Material Type and Description: [Specify material type and description.].
b. Material Standard: [Specify material standard.].
c. Manufacturer: [Acceptable to interlocking concrete paver manufacturer]]
PART 3 EXECUTION
3.01 ACCEPTABLE INSTALLERS
A. [Specify acceptable paver installation subcontractors.].
3.02 EXAMINATION
Note: The elevations and surface tolerance of the soil subgrade determine the final surface
elevations of concrete pavers. The paver installation contractor cannot correct deficiencies
17. excavation and grading of the soil subgrade with additional bedding materials. Therefore,
the surface elevations of the soil subgrade should be checked and accepted by the General
Contractor or designated party, with written certification presented to the paver installation
subcontractor prior to starting work.
A. Acceptance of Site Verification of Conditions:
1. General Contractor shall inspect, accept and certify in writing to the paver
installation subcontractor that site conditions meet specifications for the
following items prior to installation of interlocking concrete pavers.
Note: Compaction of the soil subgrade should be determined by the project engineer. If the
soil subgrade requires compaction, compact to a minimum of 95% standard Proctor density
per ASTM C 698. Compacted soil density and moisture should be checked in the field with a
nuclear density gauge or other test methods for compliance to specifications. Stabilization of
the soil and/or base material may be necessary with weak or continually saturated soils, or
when subject to high wheel loads. Compaction will reduce the permeability of soils. If soil
compaction is necessary, reduced infiltration may require drain pipes within the open-
graded sub base to conform to local storm drainage requirements.
a. Verify that subgrade preparation, compacted density and elevations
conform to specified requirements.
b. Provide written density test results for soil subgrade to the Owner, General
Contractor and paver installation subcontractor.
c. Verify location, type, and elevations of edge restraints, [concrete collars
around] utility structures, and drainage pipes and inlets.
2. Do not proceed with installation of bedding and interlocking concrete pavers
until subgrade soil conditions are corrected by the General Contractor or
designated subcontractor.
3.03 PREPARATION
A. Verify that the soil subgrade is free from standing water.
B. Stockpile joint/opening filler, base and subbase materials such that they are free from
standing water, uniformly graded, free of any organic material or sediment, debris,
and ready for placement.
C. Edge Restraint Preparation:
1. Install edge restraints per the drawings [at the indicated elevations].
3.04 INSTALLATION
Note: The minimum slope of the soil subgrade should be 0.5%. Actual slope of soil
subgrade will depend on the drainage design and exfiltration type. All drainpipes,
observation wells, overflow pipes, geotextile (if applicable) and impermeable liner (if
applicable) should be in place per the drawings prior to or during placement of the subbase
and base, depending on their location. Care must be taken not to damage drainpipes during
compaction and paving. No mud or sediment can be left on the base or bedding aggregates. If
they are contaminated, they must be removed and replaced with clean materials.
A. General
1. Any excess thickness of soil applied over the excavated soil subgrade to trap
sediment from adjacent construction activities shall be removed before
application of the [geotextile] and subbase materials.
2. Keep area where pavement is to be constructed free from sediment during
entire job. [Geotextiles] Base and bedding materials contaminated with
sediment shall be removed and replaced with clean materials.
3. Do not damage drainpipes, overflow pipes, observation wells, or any inlets and
other drainage appurtenances during installation. Report any damage
18. immediately to the project engineer.
B. Geotextiles
1. Place on [bottom and] sides of soil subgrade. Secure in place to prevent
wrinkling from vehicle tires and tracks.
2. Overlap a minimum of 0.6 m in the direction of drainage.
C. Open-graded subbase and base
1. Moisten, spread and compact the No. 2 subbase in 100 to 150 mm lifts [without
wrinkling or folding the geotextile. Place subbase to protect geotextile from
wrinkling under equipment tires and tracks.]
2. For each lift, make at least two passes in the vibratory mode then at least two in
the static mode with a minimum 10 T vibratory roller until there is no visible
movement of the No. 2 stone. Do not crush aggregate with the roller.
3. The surface tolerance of the compacted No. 2 subbase shall be ±65mm over a
3 mm straightedge.
4. Moisten, spread and compact No. 57 base in 100 mm lift over the compacted
No. 2 subbase with a minimum 10 T vibratory roller until there is no visible
movement of the No. 57 stone. Do not crush aggregate with the roller.
5. The surface tolerance the compacted No. 57 base should not deviate more than
±25 mm over a 3 m straightedge.
Note: In-place density of the base and subbase may be checked per
ASTM D 4254. Compacted density should be 95% of the laboratory index
density established for the subbase and base stone.
D. Bedding layer
1. Moisten, spread and screed the No. 8 stone bedding material.
2. Fill voids left by removed screed rails with No. 8 stone.
3. The surface tolerance of the screeded No. 8 bedding layer shall be ±10
mm over a 3 m straightedge.
4. Do not subject screeded bedding material to any pedestrian or vehicular
traffic before paving unit installation begins.
E. Permeable interlocking concrete pavers and joint/opening fill material
1. Lay the pavers [paving slabs] in the pattern(s) and joint widths shown on
the drawings. Maintain straight pattern lines.
2. Fill gaps at the edges of the paved area with cut units. Cut pavers subject
to tire traffic shall be no smaller than 1/3 of a whole unit.
3. Cut pavers and place along the edges with a [double-bladed splitter or]
masonry saw.
4. Fill the openings and joints with [No. 8] stone.
Note: Some paver joint widths may be narrow and not accept most of the
No. 8 stone. Use joint material that will fill joints such as washed ASTM
No. 9 or No. 10 stone. These smaller stone sizes are recommended for
filling joints in pedestrian applications that use 60 mm thick pavers.
5. Remove excess aggregate on the surface by sweeping pavers clean.
6 Compact and seat the pavers into the bedding material using a low-
amplitude, 75-90 Hz plate compactor capable of at least 18 kN centrifugal
compaction force. This will require at least two passes with the plate
compactor.
7. Do not compact within 2 m of the unrestrained edges of the paving units.
8. Apply additional aggregate to the openings and joints, filling them
completely. Remove excess aggregate by sweeping then compact the
pavers. This will require at least two passes with the plate compactor.
9. All pavers within 2 m of the laying face must be left fully compacted at the
completion of each day.
10. The final surface tolerance of compacted pavers shall not deviate more
than ±10 mm under a 3 m long straightedge.
11. The surface elevation of pavers shall be 3 to 6 mm above adjacent
19. drainage inlets, concrete collars or channels.
3.05 FIELD QUALITY CONTROL
A. After sweeping the surface clean, check final elevations for conformance to the
drawings.
B. Lippage: No greater than 3 mm difference in height between adjacent pavers.
Note: The minimum slope of the finished pavement surface should be 1%. The surface of
the pavers may be 3 to 6 mm above the final elevations after compaction. This helps
compensate for possible minor settling normal to pavements.
C. The surface elevation of pavers shall be 3 to 6 mm above adjacent drainage inlets,
concrete collars or channels.
3.06 PROTECTION
A. After work in this section is complete, the General Contractor shall be responsible for
protecting work from sediment deposition and damage due to subsequent
construction activity on the site.
END OF SECTION
ANNEX 2
LEED AND BELGARD SUBTERRA STONE
LEED and Belgard Permeable Paving Stone Systems
The Leadership in Energy and Environmental Design (LEED) was originally developed for
the U. S. Department of Energy. LEED utilizes a point rating system to recognize
sustainable site and building design. Many organizations were involved in developing the
rating system and certification program. The LEED program is administered by the U. S.
Green Building Council www.usgbc.org . Currently, many municipal projects that are city
owned or city funded are mandating LEED point objectives, while private sector projects
are pursuing LEED credits points on a voluntary basis.
Belgard permeable concrete paving stone systems can earn credit points in the
LEED rating system. The following listed LEED credit summaries represent possible point
contributions. Please refer to the ICPI (Interlocking Concrete Pavement Institute)
www.icpi.org Tech Spec Number 16 for a complete description and detailed explanation of
the below listed LEED Credit references. LEED Credits for new projects and major
renovations earn points from six broad rating categories and of these six, the two primary
categories that pertain to permeable concrete paving stones are Sustainable Sites (SS)
and Materials and Resources (MR).
LEED credit summaries
MR Credit 4.1: 1 point for Recycled Content 10% (post-consumer & ½ pre-
consumer)
MR Credit 4.2: 1 point (in addition to Credit 4.1) for Recycled Content 20% (post-
consumer & ½ pre-consumer)
Use materials with recycled content such that the sum of post-consumer recycled content
plus one-half of the pre-consumer content constitutes at least 10% (based on cost) Credit
20. plus one-half of the pre-consumer content constitutes at least 10% (based on cost) Credit
4.1 of the total value of the materials in the project and 20% (based on cost) Credit 4.2
of the total value of the materials in the product.
MR Credit 5.1: 1 point for Regional Materials (10% Extracted, Processed &
Manufactured Regionally)
MR Credit 5.2: 1 point (in addition to Credit 5.1) for Regional Materials (20%
Extracted, Processed & Manufactured Regionally)
Use building materials or products that have bee extracted, harvested or recovered, as
well as manufactured within 500 miles or the project site for a minimum of 10% (based on
cost) Credit 5.1 of the total materials value and 20% (based on cost) Credit 5.2 of the
total materials value.
SS Credit 6.1: 1 point for Storm Water Design: Quantity Control
Storm water management of a building site where the existing impervious area is greater
than 50% and the runoff rate and quantity is reduced by at least 25%. Belgard permeable
concrete paving stone systems can reduce runoff to zero for the most frequent storms.
SS Credit 6.2: 1 point for Storm Water Design: Quality Control
A treatment system designed to remove 80% of the average annual post development
total suspended solids (TSS), and 40% of the average annual post development total
phosphorus (TP).
SS Credit 7: 1 point for Heat Island Effect: Non-roof
Landscape and exterior designs that reduce heat island effect would entail the use of light
colored / high albedo materials with a reflectance of at least 0.3 for 30% of the sites non-
roof impervious surfaces, i.e., pavements. Manufacturing permeable concrete paving
stones in light or natural colors that can register an albedo of at least 0.3 will meet this
requirement.
Belgard
Permeable Concrete Paving Stone Systems