Facilities
G10 Site Preparation
- Site Surveying
- All new project site plans shall be developed from a new topographical map developed specifically for that project; not from "as-built" information or previous project grading plans. Accurate information is essential and "special" conditions such as asbestos, lead paint, underground tank leaks, etc. shall be addressed.
- Survey must be performed by a land surveyor with a current professional registration in the State of Alabama.
- Surveyor is to allow University Project Lead to review and comment on survey before final plots.
- Auburn University maps are based on the State Plane Coordinate system of Alabama East Zone NAD 83 (1992) and NAVD 88. Surveys and design drawings must reference this coordinate system.
- If design firm needs to create its drawings of measurement other than decimal units (such as architectural), a base point of 0,0 shall be used when rescaling the drawing. The rescaling occurs due to a change in units of measurement and is a scale factor of 12. Any scaling, rotation or change in units shall be noted in writing, on the CAD drawing, outside the plotting limits.
- An Auburn University Facilities Management checklist enumerating detailed and site specific requirements will be included in the request for proposal to perform the topographic survey. A general checklist is included in Appendix I of this document; however, consult the University Project Lead for any project specific requirements.
- Current utilities maps may be viewed in the Facilities Management Utilities & Energy. However, those maps are schematic only and are not intended to relieve the surveyor of any field verification responsibility. Verification of utilities locations shall be made through ‘Alabama 1 Call’ (800) 292-5825.
- For new facilities, evaluate the need for an archeological survey to comply with the Alabama Historical Commission policy, revised 2002.
- When surveying tree locations, the surveyor shall take three ground shots at the base of the tree trunk and three ground shots at the drip line of the tree.
- Subsurface Exploration
- Auburn University will contract directly with geotechnical consultants to perform subsurface investigations unless otherwise directed by the University Project Lead. The consultant retained for such services must be a professional engineer with current registration in the State of Alabama.
- The Designer shall coordinate with University Project Lead to develop the necessary testing locations, frequencies, depths, etc. that will be included in the request for proposal of such services.
- The contract documents shall show all boring locations, cross sections and soil reports. Also show all existing conduits, drains, utility lines, sewers, tunnels, cables, trees, paving, walks, foundations, and other objects or obstructions, whether in use or abandoned. Clearly indicate the project boundary.
- Site Clearing
- Prior to any site clearing operations the contractor shall demonstrate to the Facilities Management project manager that the ADEM “Notice of Registration”, ADEM form 4198 has been completed if required.
- All objectionable growth shall be stripped. Debris resulting from stripping and clearing operations shall be promptly removed from University property.
- Removal of trees and shrubs shall include the removal of stumps and roots to the extent that no root greater than 3 inches in diameter remains within 5 feet of neither any underground structure or utility line, nor under footings or paved areas. Grubbing in open areas shall include removal of stumps and 3 inch or greater roots to 2 feet below finish grade elevations.
- Excavations shall not be permitted which undermine the integrity of adjacent structures, paving or utilities.
- Backfill
- Backfill material shall be free of debris.
- Excess material or topsoil not required, or not permitted, as fill shall be moved to another site on University property for reuse, if directed by the University, or removed from University property at the contractor's expense.
- Specify that soils be compacted to the following minimum densities determined unless special conditions override (Percentages listed are percentage of Standard Proctor):
- Road beds and Parking areas: 95% up to 12" below subgrade, 100% for upper 12" below subgrade. Compaction is required for the entire subgrade area for the full width and depth of slope of embankments supporting berms and pavement.
- Under non-structural slabs on grade with normal loading inside the structure: 95%.
- Under foundations, isolated pads, and footings: 100%.
- Foundation backfill under planting beds and lawn: The upper 2 feet of soil below finish grade - 90% maximum with remainder of backfill being 95% if depth is less than 10 feet and 100% if depth exceeds 10 feet.
- Foundation backfill under pavements: 100%.
- Under paved pedestrian walks and courts: 95%.
- Backfill around manholes and other underground structures: 95% if depth is less than 10 feet; 100% if depth is more than 10 feet.
- Under lawn and planting areas not adjacent to structures: The upper 1 foot of soil below finish grade - 90% maximum. Remainder - 95%.
- Extreme care shall be taken to obtain proper compaction in areas which abut walls, curbs, adjacent slabs, and other structures where use of mechanical compactors is difficult.
- Field compaction tests and related laboratory analyses shall be performed by a qualified independent laboratory (conforming to American Society for Testing and Materials standards), under the supervision of a registered professional engineer specializing in soils engineering. Soils proposed for fill, backfill, and embankments shall be analyzed by the soils engineer to determine acceptability; no soil shall be placed until it is approved by the soils engineer. A representative of the testing laboratory shall provide continuous inspection during placement and compaction operations; tests shall be made in a quantity that will assure uniform compaction and density of each course or lift of fill.
- The University solicits proposals for the testing laboratory shortly after the receipt of construction bids. The designer shall contact the University prior to this time regarding any specific requirements for the proposal request.
- Tree and Plant Protection
- A tree protection plan shall be provided for each project as determined by University Project Lead and Facilities Management Landscape Services. The intended protection is to be shown on the Erosion and Sediment Control: Pre-Construction Site Plan Drawing. It is desirable to save existing trees whenever possible. During design, the University Project Lead, with help from Facilities Management Landscape Services, shall identify specifically those trees to be saved and those which must be removed. Trees which must be damaged by construction to the point that they have little chance to survive shall be considered for removal.
- All trees to remain are to have protective barriers set outside the drip line of the tree or using the following formula: (Zone of Tree Protection from Trunk (ft)) = (Tree diameter at breast height (in)) X 1.5, whichever is larger.
- Barriers shall be installed prior to any construction and shall remain until construction and site cleanup is complete. The barriers shall be of substantial material: 4 X 4 posts with 2 X 6 rails set at a minimum height of four feet. No construction material, debris or excavated material shall be stored within the barricade area. The barriers shall be steel post at 8’-0” O.C. with wire ties in posts at 12” O.C. barrier material to be 4’ tall orange high density polyethylene safety and barrier fencing. The top of the fencing shall be supported with chain link, galvanized tension wire. In the alternative, chain-link fencing may be used. Fencing shall be maintained in good condition for duration of project.
- No construction material, debris or excavated material shall be stored within the barricaded area. No vehicles, trailers, etc. shall be parked inside the barricaded area.
- Each barrier shall have on all sides, a mounted sign reading in English and Spanish “KEEP OUT” “NO ENTRA” (3 inch lettering) and “TREE PROTECTION” “PROTECCIÓN DE ÁRBO” (¾ inch lettering).
- Protect root system from flooding, erosion and noxious materials in solution from spillage of construction materials.
- Care must be taken in excavating foundations and installation of utility lines adjacent to trees that are to be saved.
- Excavate within drip line of trees only where indicated on plans. If excavation will damage trees extensively, the trees shall be removed and replaced.
- Where trenching for utilities is required within the drip line, tunnel under or around roots by hand digging. Do not cut main lateral or tap roots. Cut smaller roots which interfere with a sharp pruning tool; do not chop or break.
- Do not allow exposed roots to dry out before backfill is placed; provide temporary earth or moist burlap cover.
- Any tree to remain that has had excavation within the drip line shall be pruned by a professional arborist according to the National Arborist Association Standards Class IV - Cutting Back or Drop Crotch Pruning
- Cutting back or drop crotch pruning shall consist of the reduction of tops, sides, under branches or individual limbs. This practice is to be undertaken only in cases of utility line interference, or where certain portions of the roots or root systems have been severed or severely damaged.
- The following specifications shall apply:
- All cuts shall be made sufficiently close to the trunk or parent limb, without cutting into the branch collar or leaving a protruding stub, so that closure can readily start under normal conditions. All cuts shall be clean. It is necessary to precut branches too heavy to handle to prevent splitting or peeling the bark. Where necessary, to prevent tree or property damage, branches shall be lowered to the ground by proper ropes or equipment.
- Remove the weaker, least desirable, crossed or rubbed branches. Such removal shall not leave holes in the general outline of the tree.
- Generally, in reducing size (cutting back) not more than one-third of the total area shall be reduced at a single operation. When cutting back, only drop crotch as much as necessary. Where practical, avoid cutting back to small suckers. All effort shall be made to cut back to a lateral, one-third the diameter of the cut being made. In reducing overall size, attention is to be given to the symmetrical appearance. Top is to be higher and sides reduced in order to maintain a tree-like form. When cutting back trees, one shall have in mind to make them shapely and typical of their species.
- On thin bark trees, just enough limbs shall be removed to get the effect wanted without admitting too much sunlight to the trunk of the tree or the top of large branches. Care shall be taken with the following species: lindens, maples, beeches, apples, oaks, and other trees susceptible to sunscald, growing in different geographical areas. The damage may be minimized by doing work on susceptible species during the dormant season.
- In lifting the lower bottom branches of trees for under clearance, care shall be given to symmetrical appearance, and cuts shall not be made so large that they will prevent normal sap flow.
- Periodical drop crotching or cutting back of silver maples, poplars, and other trees with brittle and soft wood is an established practice and has proven beneficial in maintaining the safety of these trees over long periods of growth. Other trees with soft and brittle wood growing in different geographic areas may be specifically named when it is common practice to control growth by cut-back. An alternate method in some situations for maintaining the safety of these trees would be cabling and bracing.
- Maintain existing grade outside drip line of trees, unless otherwise indicated on plan. Do not leave open excavations in the vicinity of protected trees for longer than 2 days to prevent soil moisture reduction.
- Fertilization
- Where tree roots within the drip line will be covered with asphalt or concrete, feeders shall be installed as recommended by the National Arborist Association Standards.
- Install extended feeders where construction of wells or retaining walls is required within the drip line.
- The design must provide a yard hydrant, irrigation system or other convenient water source adjacent to trees that remain.
- The specifications shall define proper fertilization and the contractor shall fertilize affected trees during construction.
- Repairs to Damaged Trees
- Repairs to damaged trees shall be performed by a professional arborist.
- Trees damaged beyond repair or that do not survive will be removed by the contractor. A replacement cost will be determined by a professional arborist and paid by the contractor. The University will reserve the option of having the contractor replace the tree with one of equal size and quality.
- Grading
- Finish grade slopes shall be shallow enough to allow mowing (generally 1:3 or less); steeper slopes will be permitted only in areas where maintenance-free erosion control (groundcover planting, rip-rap, etc.) is planned.
- All areas disturbed by construction operations and not covered by building, paving, etc. shall be fine graded and temporarily seeded. Sod is to be used for permanent lawns.
- Demolition
- Foundations of demolished structures shall be completely removed.
- Every reasonable effort shall be made to avoid blasting if structure to be demolished is in close proximity to other structures. If blasting is utilized, control dust and excessive noise when surroundings require. Document conditions of adjacent structures when collateral damage is possible. Seismographic monitoring may be required on adjacent buildings. Prior approval is required for any blasting demolition.
- Site Remediation
- Hazardous materials survey and remediation are assumed to be separate from building design unless otherwise requested by the University Project Lead and/or Risk Management and Safety.
- Auburn University will contract directly with environmental consultants to perform the necessary assessments and remediation, if applicable. The consultant retained for such services must be a professional engineer with current registration in the State of Alabama in addition to any certifications required by local, state, and federal regulatory agencies.
- Erosion control
- General
- See Appendix N for Erosion and Sediment Control Process Narrative.
- The methods of erosion and sediment control outlined in this document are not intended to limit engineer creativity and innovation. The listed methods are intended to create a uniform set of standards for designers and contractors to use, to ensure a maximum level of erosion and sediment control is achieved. Any desire to deviate from the standards should be presented to the Auburn University Project Lead.
- All design and construction activity must be performed in compliance with the most current ALOA Erosion and Sediment Control Policy as provided by the Department of Risk Management and Safety, in addition to complying with all local, state, and federal regulatory requirements.
- The Auburn University Design and Construction Standards are more stringent and shall to be used to supplement the Alabama Department of Environmental Management (ADEM) requirements regarding construction site storm water run-off.
- Designers and contractors should be familiar with The Alabama Handbook for Erosion and Sediment Control and Storm Water Management of Construction Sites and Urban Areas which can be obtained at no cost at (www.swcc.state.al.us). Portions of this handbook are referenced in the Auburn University Design and Construction Standard.
- All construction sites on campus, regardless of size, will be subject to the design requirements here-in. Auburn University reserves the right to waive the requirements of this document should the University Project Lead deem it appropriate.
- All Alabama Department of Environmental Management (ADEM) and National Pollutant Discharge Eliminations Systems (NPDES) permitting and sampling documentation must be prepared by the civil engineering consultant. The civil engineering consultant must be a registered professional engineer in the State of Alabama as well as meeting any other requirements of a certifying professional as set forth by ADEM. Additionally, the civil engineering consultant shall be familiar with Auburn University’s additional erosion and sediment control standards located here-in.
- The Design Return Period Storm for sizing Erosion and Sediment Control Measures shall be a 25 year-24 hr storm.
- Before initiating any earthwork not directly associated with the installation of erosion and sediment control measures as indicated on the pre-construction erosion control plan, the Contractor will be required to acquire a “Land Disturbance Authorization” form from an Auburn University representative. (see Appendix N for form) The Contractor shall be responsible for obtaining a “Notice of Registration” from ADEM. The Contractor shall provide proof of ADEM registration to the Auburn University Construction project manager prior to receiving the “Land Disturbance Authorization” permit.
- The Contractor shall be responsible for all monitoring, inspections, etc. to assure the Owner that the site is at all times in accordance with ADEM Rules and Regulations. Documentation of QCI and QCP inspections shall be provided to the Owner.
- In addition to the inspection, monitoring requirements instituted by ADEM, Auburn University is requiring that the storm water outfall from any construction site on campus have a turbidity of not more than 50 NTUs (Nephelometric Turbidity Units) for any 25 year, 24-hour event and smaller.
- If United States Corp of Engineers approved construction is to be performed in any stream bed, the increase in turbidity from the upstream or “background” flow to the downstream flow shall be no greater than 50 NTUs.
- Auburn University will conduct inspections monthly, after each ½” rain event, and prior to any substantial predicted storm event to ensure the contractor is properly maintaining erosion and sediment control. ADEM is to be notified if any sites are found to be non-compliant during these inspections.
- Auburn University will sample and record turbidity throughout the life of the project to determine whether the civil engineer and contractor have properly designed and installed the Erosion and Sediment Control Measures.
- The contractor will be responsible for any incurred regulatory fines throughout the course of construction.
- Auburn University reserves the right to withhold retainage for all but not limited to the following: Failure to maintain erosion & sediment control measures, the inability to meet Auburn University’s turbidity sampling requirements, services rendered by Auburn University in the event that a contractor is unresponsive to directives to modify erosion and sedimentation control measures. Auburn University also requires the Designer of Record to incorporate site specific Erosion and Sedimentation Control measures as unit prices in the bid package. These unit prices will be implemented in the event the site requires additional protection or if the contractor is nonresponsive to Erosion and Sedimentation problems that occur. These unit prices can also be implemented negatively if the contractor has not met his contractual obligations. Thus allowing the owner to have the BMP’s installed by other means.
- There shall be in ALL Construction drawing sets requiring an Erosion and Sediment Control Plan, a sheet of general notes for erosion and sediment control.
- Following each phase of the Erosion and Sediment Control Plan there shall be a sheet of project applicable details that correspond to the erosion and sediment control best management practices. These details are to be obtained from Auburn University. (see Appendix N)
- All disturbed areas must be protected with temporary seeding within 13 days of the latest disturbance.
- It will be imperative that sediment laden runoff not be allowed to enter any pervious pavement areas. These areas shall be protected, at minimum, using a silt fence located up slope of diversion wales.
- Auburn University strongly encourages designers and contractors to consider the use of processed demolished building debris for appropriate erosion and sediment control measures such as check dams, construction exit pad, temporary roads, ditch lining, outlet protection, and inlet protection.
- Erosion and Sediment Control Plan
- The Erosion and Sediment Control Plan is a set of drawings which provides the necessary measures to reduce erosion on construction sites and minimize the impacts of sediment, turbidity and hydrologic changes off-site throughout the life of the project and beyond. It is to ensure that erosion and sediment control is appropriate for the planned use of the site.
- The Erosion and Sedimentation Control Plan shall follow the Alabama Handbook for Erosion Control, Sediment Control, and Storm Water Management on Construction Sites and Urban Areas and must be reviewed and approved by Auburn University Office of Risk Management & Safety and Auburn University’s erosion control consultant.
- Required content of the Erosion and Sediment Control Plan
- See Appendix N for standard notes.
- Site Map Drawing
- This Sheet to resemble the drawing required by ADEM for NPDES permitting, placed on a USGS 7.5-minute Topographic Quadrangle)
- Receiving waters labeled
- Site discharge points indicated
- Point of entry into receiving waters indicated
- Pre-Construction Site Plan Drawing
- Note: This plan to show necessary erosion sediment control measures to be installed before land disturbance authorization is granted. Only grading specifically identified as intended for erosion and sediment control shall be permitted prior to land disturbance authorization.
- Contours, existing and proposed
- Placement of necessary erosion & sediment control BMPs
- Tree protection
- Discharge points
- Expected pre & post-construction flow discharges for 25 year-24 hr event (in table format)
- Site specific notes
- Note referencing the full sheet of general notes
- Erosion and sediment control details
- Construction Site Plan Drawing
- Phasing of changes to erosion and sediment control BMPs
- Contours, existing and proposed
- Placement of erosion & sediment control BMPs
- Tree protection
- Site specific notes
- Note referencing the full sheet of general notes
- Erosion and sediment control details
- Post-Construction Site Plan Drawing
- Note: This plan to show necessary Erosion Sediment Control Measures to be installed before substantial completion to be awarded.
- Contours, existing and proposed
- Changes to erosion and sediment control BMPs
- Site specific notes
- Note referencing the full sheet of general notes
- Erosion and sediment control details
-
- Erosion and sediment control BMPs, details:
- This section outlines the design requirements and appropriate applications for Erosion and Sediment Control Practices on Campus. The acronym in parentheses, following the practice or device, corresponds to the associated detail.
- Site Preparation
- AutoCad details provided in Appendix N.
- Construction Exit Pad (CEP)
- Practice Description
- Construction exit pads are used to prevent sediment from leaving the site by means of the wheels of construction vehicles exiting the construction site.
- Stone shall be ALDOT No. 1 (1” to 3” inch stone)
- Pad shall be 6 inches thick.
- Pad shall be a minimum of 50 feet long and 20 feet wide.
- If stone alone does not sufficiently remove sediment, vehicle tires should be washed before exiting site with sediment-laden runoff draining into an on-site sediment trap or basin.
- Geotextile selection shall be in accordance with AASHTO M288.
- Should the construction exit pad cease to effectively remove tire born sediment, the top 3 inches of stone shall be removed and replaced.
- Land Grading
- The practice of modifying existing topography for desired land uses.
- Grading plans should be designed to protect existing vegetation where possible.
- Grading should be scheduled to minimize the amount of time disturbed areas are left exposed to erosion elements.
- The grade of slopes (excluding channel side slopes) on campus should, as a general practice, be no greater than 3 horizontal feet to 1 vertical foot (3:1).
- Retaining walls should be incorporated into the design where site conditions require grades of steeper than 3:1.
- Top soil from areas to be graded shall be removed and stockpiled for reapplication upon completion of grading operations. A stockpile location should be suggested by the engineer. Stockpiled vegetation should be protected from erosion by temporary vegetation.
- Slope lengths on site should be minimized by the use of diversion channels. Recommendations for diversion placement are given in the table below.
|
Slope
|
Spacing (Ft)
|
|
33-50%
|
20
|
|
25-33%
|
40
|
|
15-25%
|
60
|
|
10-15%
|
80
|
|
6-10%
|
120
|
|
3-6%
|
200
|
|
<3%
|
|
- Where practical, storm water run-on from adjacent undisturbed sites should be diverted around the construction area to minimize on-site erosion.
- Top Soiling (TSG)
- The removal of soil surface useful for establishing vegetation. This practice is applied to areas to be disturbed by excavation, compaction, and general grading operations. Top soil is generally darker than subsoil due to increased levels of organic matter. This soil, upon distribution over the disturbed site is advantageous for establishing vegetation to minimize erosion.
- Topsoil shall be relatively free of debris and shall give evidence as a suitable soil for growing vegetation prior to stripping.
- pH should be in the range of 6.0-7.0. Any pH below 6.0, shall result in the addition of lime in accordance with a soil test report.
- Soluble salts levels shall be below 500 ppm.
- Depth of material placed on site meeting the above requirements should be 4 inches.
- Tree Protection (TP)
- Protection of the trees at Auburn University is an extremely important consideration of any design. The university greatly values the trees on campus and will seek monetary reparations for any unnecessary damage incurred. Tree protection entails the clear marking and barricading of protection zones around all trees in a project area that are to remain untouched.
- See Section 5, this document.
- Surface Stabilization
- Chemical stabilization of disturbed slopes can be achieved through the use of an anionic polyacrylamid or PAM. It is typically applied in conjunction with seeding and mulching to help quickly establish permanent slope stabilization through vegetation.
- Only the use of anionic PAM is permitted. Cationic PAM is toxic to fish and shall not be used.
- Application rates shall conform to manufacturers’ guidelines.
- Follow requirements of the material safety data sheet.
- The maximum application rate of pure PAM shall be 200 pounds/acre/year for PAM used as a flocculent, see Section 9.3.4. second bullet -Flocculants
- Use dust control techniques used to prevent windborne soil particle (dust) from leaving the construction site. The most effective form of dust control is to disturb the minimal area necessary for work at a given time especially during drought conditions.
- Vegetative cover- See Permanent Seeding Section 9.3.3. eleventh bullet.
- The use of stone can stabilize roads and reduce dust production by vehicle traffic.
- PAM serves as a temporary soil binder. See Chemical Stabilization Section. 9.3.3. sixth bullet.
- Tilling the soil brings the moist layer of subgrade to the surface to reduce dust production.
- Sprinkling the site by water truck until surface is wet or irrigating with a fixed sprinkler are acceptable ways to prevent dust production.
- Erosion Control Blanket (ECB.A)
- A protective cover for exposed slopes used to aid in establishment of permanent vegetation. Erosion control blankets are utilized on steep slopes or in environments that might not be conducive to expedited establishment of vegetation. Blankets are typically comprised of plant fibers, plastic, or nylon. Erosion control blankets are also used for protecting soil in concentrated flow areas.
- Design Criteria
- Slopes steeper than 5:1 (20%) shall be protected with an ECB.
- ECBs shall have evenly distributed organic material.
- ECBs shall be a minimum of 48” in width.
- ECBs are to be installed with the fall of the slope, never across the slope.
- Regarding staking, install ECBs in accordance with ECB detail.
- Due to the excessive amount of erosion control blankets available, specific discussion of each type of blanket will not be described in this manual. Manufacturer’s guidelines should be followed when selecting the appropriate ECB.
- Refer to the Alabama Handbook for Erosion and Sediment Control for the material requirements for various applications.
- Soil Guard (ECB.B)
- Soil guard bonded fiber matrix is an acceptable alternative to erosion control blankets. Soil guard is hydraulically applied, conforming to contours of the slope before hardening into a fiber matrix which holds seed and soil in place. As seeds germinate the biodegradable matrix breaks down. Soil Guard is to be used for protecting slopes and sedimentation/retention basins from rainfall and wind erosion.
- Follow manufacturer and certified applicator guidelines for design mix and proper application.
- Typical drying time is 12-24 hours.
- Expected application life is 9 months.
- Typical application rate 3000-4000 pounds/ acre.
- Soil Guard is not for use in concentrated flows.
- After installation, soil guard protected slopes shall be kept free of foot and vehicle traffic until after seed germination.
- Hydro-Seeding
- The planting process which utilizes a liquid mixture of seed and mulch. This “slurry” is sprayed on the desired area to produce a vegetative cover. The slurry also can include fertilizers, green dyes, and tackifiers for improved vegetative yields.
- Manufacturer recommendations and soil test reports should be utilized when determining an appropriate hydro-seeding mixture.
- Mulching (MU)
- The application of plant material over the soil surface to reduce overland flow velocity of storm water runoff and to reduce the eroding effects of raindrop impact. It is also used to protect seed and establish plant cover. Mulching can be applied by hand or with a mulch blower.
- See Hydro-seeding for alternative to mulching.
- Mulching shall be in accordance with ALDOT Spec Section 860, Class A.
- Mulching should be applied after grading and seeding.
- Use hay, straw, or wood chips on campus.
- Apply until 80% ground cover is achieved.
- All straw shall be crimped (anchored) to hold mulch in place.
- Suggested mulching application rates

- Permanent Seeding (PS)
- Vegetation is the best long term method for preventing erosion.
- Bermuda grass is typically used on campus. Refer to ALDOT Spec Section 860 for Bermuda grass seeding requirements.
- Vegetation selection should be coordinated with the Auburn University Landscaping Division.
- It is the responsibility of the contractor to choose a seed that will germinate to provide a good stand of grass.
- A ground cover of 95% must be achieved before final completion will be awarded.
- Rip Rap
- Rip Rap is typically used at pipe outlets, channel linings, and for steep slopes. Rip Rap shall be used permanently, only as outlet protection and channel lining for Auburn University.
- The purpose of Rip Rap is to provide slope erosion protection from swift moving water. Rip Rap should be used for channels with a full flowing velocity between sand 10 ft/s for a 25 yr, 24 hr storm event or for stabilizing cut and fill slopes.
- Use ALDOT specifications section 610.03(b) to select the proper geotextile material to install between Rip Rap and the soil base.
- Rip Rap should be sized for channels at full bank flow. Use Table below for sizing Rip Rap and Filtering Stone for Rock Filter Dams.
- Do not place Rip Rap on slopes steeper than 1.5 ft/ft.
- Thickness of Rip Rap linings should be 1 to 1.5 times the maximum size stone in the gradation.
- Special consideration should be given to the use of processed demolished building debris for appropriate erosion and sediment control measures such as check dams, construction exit pad, temporary roads, ditch lining, outlet protection, and inlet protection.
- Filter stone is for placement on the upstream face of rock filter dams. Graded Rip Rap stone for channel lining and outlet protection.
|
Flow Velocity
(ft./sec.)
|
ALDOT No.
|
Size Inches
(Sq. Opening)
Max. Avg.2 Min.
|
ALDOT
Filter Stone No.
|
|
2.5
|
5
|
1 ½
|
¾
|
No. 8
|
810
|
|
4.5
|
24
|
3
|
1 ½
|
1
|
810
|
|
6.5
|
1
|
6
|
3
|
2
|
8
|
|
9.0
|
Class 1 Rip Rap
|
12
|
6
|
3
|
1
|
|
11.5
|
Class 2 Rip Rap
|
18
|
9
|
5
|
1
|
|
13.0
|
Class 3 Rip Rap
|
24
|
12
|
7
|
1
|
- Maximum stone Size for Rip Rap lining of channels and outlets.


- Sodding (SOD)
- The installation of transplanted vegetative cover. The intent is to provide immediate erosion control for disturbed soils. Areas benefiting from the use of sodding are diversions, adjacent to storm drain inlets and outlets, and disturbed slopes.
- Bermuda grass is the standard species used for sodding on campus.
- A soil test should be performed to determine any necessary soil amendments to facilitate growth. Soil tests are to be conducted by Auburn University Soil Testing Laboratory.
- Before installation, the soil should be cleared of debris and clods larger than 2” in diameter.
- Low spots are to be removed to prevent ponding.
- Prepare soil by disking and rolling.
- Limit the use of heavy equipment to avoid over-compacting the soil and creating a root barrier.
- Temporary Seeding
- The establishment of rapidly growing vegetation to stabilize disturbed area and prevent soil erosion until permanent plantings can be installed. Temporary seeding is used when work ceases temporarily or when work is completed in a season not suited for final planting. Temporary seeding shall meet the requirements of ALDOT Specification Section 860.01.
- Temporary seeding greatly reduces silt accumulation based maintenance of sediment control devices.
-
- Hay Bale/Waddle Check Dam (HBCD)
- A row of straw bales or waddle (silt sock) entrenched in a storm water conveyance channel with the purpose of removing sediment from the construction site’s storm water runoff.
- The low flow rate of straw bales often leads to ponding and overtopping of bales. Be aware of ponding water concerns when including straw bales in an erosion control plan.
- Bale dimensions should be 14” x 18” x 36”.
- Bales should be embedded 4” into the soil and staked, using 2, 2” x 2” hardwood stakes.
- Hay bale check dams should be spaced at the horizontal distance that corresponds to one vertical foot of elevation change.
- Typical useful life of a straw bale is 3 months.
- Waddles with a 10” diameter, are acceptable alternatives to hay bales.
- Hay or coconut fiber waddles should be staked along both sides of the length of the waddle with a spacing of four feet.
- Stakes should be angled away from the waddle to resist upward force applied to the waddle by the flow of water.
- Diversion Channel (DV)
- A temporary or permanent excavated channel designed to collect storm water and divert it away from the disturbed site to prevent erosion damage. Diversions can be used to intercept storm water running onto a site and eliminate the need for sediment removal for a potentially substantial volume of water. Rapid establishment of vegetation is crucial to proper diversion function.
- Temporary storm water diversions shall be capable of carrying a 25yr, 24hr storm event with a 0.3 foot freeboard.
- Permanent storm water diversions shall be capable of carrying a 50yr, 24hr storm event.
- Recommended spacing of storm water diversions
|
= Slope
|
Spacing (Ft)
|
|
33-50%
|
20
|
|
25-33%
|
40
|
|
15-25%
|
60
|
|
10-15%
|
80
|
|
6-10%
|
120
|
|
3-6%
|
200
|
|
<3%
|
|
- Refer to the Alabama Handbook for Erosion and Sediment Control for guidance regarding further information on storm water diversion design.
- Inlet Protection (IP)
- Inlet protection is intended to reduce the amount of sediment entering a pipe such as a culvert. Inlet protection is achieved using the hay bale check dam.
- See hay bale check dam section.
- Outlet Protection (OP)
- Practice applied whenever a high velocity discharge must be released onto an erodible soil, typically at the outlet of a channel or conduit. Protection is achieved by means of a Rip Rap lined apron, concrete baffles, and concrete flumes.
- The outlet protection for Auburn University should be designed to handle the peak storm water runoff from a 25 yr, 24hr storm.
- The Alabama Handbook for Erosion and Sediment Control provides precise design requirements for outlet protection.
- Sediment Control
- For Storm Water Detention See G-30 Section 4.3.1
- Flocculants
- Floc-logs are a semi-hydrated polyacrylamide blended block that when placed within turbid water flows will remove fine particles and reduce NTU values.
- Soil Tests are required in order for the manufacturer to select the proper Floc Log mixture.
- Placement of Floc Logs should be as close to the source of particle suspension as possible.
- Floc Logs can be placed in the invert of drop structures to begin treating sediment-laden water immediately upon entering the collection system. This application is only acceptable if the collection system in which the Floc Log is placed flows into a temporary sedimentation basin.
- Floc Logs can be placed in the invert of open ditches directly behind check dams and well upstream from the sedimentation basin. This application is only acceptable if the collection system in which the Floc Log is placed flows into a temporary sedimentation basin.
- The use of Floc Logs should be considered in any application in which storm water is detained at a sediment trap before entering the storm water collection network. These traps include excavated drop inlet protection, hay bale check dams, rock filter check dams, and sedimentation basins.
- The typical flow treated by one Floc Log is 60-75 GPM.
- Floccin Bags
- A manufactured bag filled with the Floccin Flocculating Agent that when placed within turbid water flows, causes suspended soil particles to coagulate and drop from solution, therefore reducing NTU values.
- Always follow manufacturer’s dosing recommendations.
- Place Floccin Bags as far upstream from the sedimentation basin as feasible to allow more time for mixing and sediment deposition.
- Floccin Bags are typically staked to the ground in the invert of the ditch immediately following a check dam.
- The use of Floccin Bags should be considered in any application in which storm water is detained at a sediment trap before entering the storm water collection network. These traps include excavated drop inlet protection, hay bale check dams, rock filter check dams, and sedimentation basins.
- Flocculant Covered Fabric at Check Dams
- A practice similar to the use of Floc Logs. Polyacrylamide in the form of an emulsified powder is applied to a moist coir fabric attached to the downstream side of check dams in open channels and is used to facilitate sediment deposition and reduction of the NTU value of discharged storm water.
- The powder form of polyacrylamide should be applied to a secured, moist fabric, typically 700-900 g/m2 Coir, on downstream face of Check Dam, either Rock or Hay.
- Follow manufacturer guidelines for dosing.
- Grate Inlet Protection in Pavement
- A sediment barrier formed from filter fabric, gravel, hay or coconut waddles, and sand bags used to minimize the amount of sediment entering an inlet. This method can be used in paved inlets. This method is for protecting inlets with no bypass (inlets in a sag). It can also be used for inlets in disturbed area, but fabric drop inlet protection is preferred.
- Drainage area should be less than 1 acre.
- The approach slope to the inlet should be less than 1%.
- Used for inlets in sag, with no bypass.
- Height of gravel should be 0.5’ high.
- Gravel should have a 2:1 side slope or flatter.
- #57 washed stone is recommended for the gravel.
- Curb Inlet Protection (CIP)
- Type “S” Curb inlets located in paved areas within the same drainage basin as the construction site require protection from sediment laden storm water flowing along the curb and gutter. Type “S” curb inlets constructed prior to paving that are in disturbed areas require either fabric drop inlet protection or block and gravel protection. Curb inlet protection can potentially lead to flooding of roadways. Should unsafe driving water conditions be created due to water standing in roadways remove the inlet protection immediately.
- Use 10” diameter hay or coconut fiber waddles.
- Waddles are to be held in place by weighting with sand bags or bags of stone.
- Place waddles in gutter and at a minimum of 1 foot from the inlet throat. This allows overflow and prevents flooding.
- Alternatively, the practice of wrapping 8” concrete blocks with silt fence material is also an acceptable form of inlet protection.
- Fabric Drop Inlet Protection (FIP.1 and FIP.2)
- New and existing drop (grate) inlets in disturbed areas (do not use in paved areas) must be protected in order to minimize the amount of sediment laden water from entering the storm water collection network. This can be achieved through manufactured products or constructed on site. This method can be combined with the excavated drop inlet protection (XDIP) for even better results.
- Design Criteria-Silt Fence with Wood Supported Frame (FIP.1)
- Use only in locations with a drainage basin slope of 5% or less.
- This method is not applicable to inlets receiving concentrated flows.
- Silt fence type A shall be used for this application.
- When sediment has accumulated to ½ the height of the structure, it should be removed and properly disposed.
- See detail for dimensioning
- Design Criteria- Frame and Filter Fabric (FIP.2)
- Use only in locations with an approach slope of 2% or less.
- Drainage area should be less than 1 acre per inlet.
- Frame shall be constructed of high density polyethelene copolymer (HDPE).
- Frame may be round or square base.
- The fitted filter assembly shall be constructed of 100% continuous polyester needle-punched non-woven engineering fabric and follow the guidelines in the American Society for Testing and Materials (ASTM) D1117-99.
- The filter fabric shall have a weight on no less than 2.5 ounces per square yard.
- The filter fabric shall have a tensile strength of no less than 70 psi with an elongation at break of no less than forty percent (40%).
- The filter fabric shall have a minimum U.V. rating of no less than 65% at 500 hrs.
- Filter fabric flow shall be no less than 100 gallons/minute/ft2 at the time of installation
- Filter fabric shall have minimum puncture strength of 40psi.
- Filter fabric shall be composed of 2-stages (D.O.T. Filter). The lower half of the frame supported fabric shall be a 100 gallons/minute/ft2 “low-flow” fabric, while the upper half allows a greater flow to pass through reducing flooding risks.
- When sediment has accumulated to ½ the height of the structure, it should be removed, re-deposited, and stabilized on the site.
- Excavated Drop Inlet Protection (XDIP)
- The excavated drop inlet is the preferred method of sediment control for grate inlets and open throat inlets placed in unpaved areas. The excavated drop inlet method of protection is the creation of a small sediment basin around a drop inlet in an unpaved area that is allowed to dewater through weep holes cored in the sides of the inlet structure. The sediment laden water is filtered through stone and filter fabric before entering the structure. The detention time allows for sediment deposition. Should the weep holes become fouled, the structure will overtop and allow water to enter through grating or the open throat.
- The excavated basin shall have a maximum depth between 1 and 2 feet.
- Minimum diameter of the excavated sediment trap, at rim elevation, shall be 12 feet at minimum.
- The sediment trap shall be sized to hold 67 cubic yds per disturbed acre.
- Side slopes for the basin shall be 2:1 or flatter.
- The inlet structure shall at the level of the bottom of the sediment trap, have 4, 2” holes (16 total) cored into each side of the structure.
- Type A silt fence shall be wrapped around the structure with the weep holes covered by no less than 1foot in any direction.
- Install washed No. 57 stone around the structure to provide protection for the silt fence. The minimum width of the stone filter around the structure shall be 2 feet.
- If inlet drains more than 1 acre use fabric drop inlet protection in conjunction with the excavated drop inlet protection.
- Remove sediment when accumulation reaches one half the depth of the excavation.
- Rock Filter Dam (RFD)
- Rock filter dams are temporary stone filter dams placed in drainage ways, concrete lined or vegetated, to slow the flow of water by dissipating energy and thereby reducing drainage way erosion and allowing for a reduction in turbidity by increasing the available time for soil particles to settle out of suspension. Rock filter dams are commonly placed upstream of sediment ponds to remove courser particles of sediment.
- Rock filter dams are utilized only for drainage areas of 10 acres or less. Rock filter dams are used as a finishing tools and work efficiently only if the majority of sediment is removed from storm water before entering the drainage way.
- Dam height should not exceed the elevation of the upstream 6” below half the ditch height.
- Spacing of rock check dams should be such that the crest of the downstream dam is at the same elevation as the base of the upstream dam.
- Stone should be sized using the Rip Rap section of this document. The upstream face should contain smaller stone to facilitate the filtering process.
- For additional sedimentation benefits, install jute mats 700-900 g/m2 on downstream face of a Rock filter dam and while wet, spread PAM over jute mats in accordance with manufacturer’s guidelines. Alternatively, fix “floc-logs” or “floccin bags” in place on the tailwater side of Rock Filter Dam.
- Sediment Basin (SBN)
- Sediment basins are typically employed for large disturbed areas or when the use of smaller localized sediment traps would not provide adequate protection.
- Sediment basins are earthen embankments used to detain sediment laden storm water in order to provide adequate time for soil particles to settle out of suspension. Water at the surface of the pond is the most treated and least turbid. Therefore the storm water is dewatered from the top of the pond by utilizing a skimmer (floating weir). The process is made more efficient through the use of a flocculant to improve sedimentation and baffles for dechannelizing the flow within the pond. Sediment ponds are often converted to storm water detention or retention ponds after the construction phase is complete in order to manage post-construction storm water runoff.
- The Alabama Handbook for Erosion and Sediment Control and Storm Water Management of Construction Sites and Urban Areas provides detailed guidelines for the design and construction of sediment basins. Specifics for the design on Auburn University’s campus are listed below.
- Minimum basin width shall be 10 feet (toe of slope to toe of slope).
- Preferred length to width ration is 3:1. When site constraints do not permit a 3:1 ratio, an absolute minimum length to width ration of 2:1 may be used.
- The minimum depth of the basin shall be 4 feet.
- Basin side slopes shall be 2:1 or flatter.
- The basin shall hold and store at minimum 3600 cubic feet/acre of drainage.
- Sediment ponds shall be designed to treat storm water run-off of a 25 year, 24 hr storm.
- Basin and skimmer should be designed to store and dewater a 25 year storm event over 3 days.
- Floating skimmers shall be the primary method for dewatering the sedimentation basin. Perforated riser designs will not be accepted.
- The emergency spillway shall be sized for storm water run-off flows from a 50 year, 24 hr storm.
- The emergency spillway may be designed as an overflow channel lined with Rip Rap or a self-cleaning drop inlet structure.
- PAM shall be used to increase the soil particle deposition rate in the sedimentation basin. Preferred methods include the use of fixed “floc logs” or “floccin bags” at the inlet of the basin, or placement of PAM emulsions or powders on the first baffle of the basin.
- Dewatering-Dirt Bag (DB)
- For temporary dewatering operations the use of a “DIRTBAG” may be employed. The sediment laden water is filtered as it is forced through the porous geotextile fabric of the bag. Filter socks are not acceptable alternatives to dirt bags.
- Composition shall be polypropylene nonwoven geotextile
- Spout shall be capable of receiving a 4” discharge hose
- Place dirt bag on slopes no greater than 2%.
- Orient the inlet of the bag facing up-slope.
- Place bag on 6 inch thick bed of gravel or bed of wooden pallets to allow more rapid dewatering.
- Minimum Material Requirements for DIRTBAG
Property Test Method Units Test Results
Weight ASTM D-3776 oz/yd 7
Grab Tensile ASTM D-4632 lbs. 200
Puncture ASTM D-4833 lbs. 100
Flow Rate ASTM D-4491 gal/min/ft2 80
Permittivity ASTM D-4491 sec.-1 1.1
Mullen Burst ASTM D-3786 lbs. in2 340
UV Resistant ASTM D-4355 % 65
AOS % Retained ASTM D-4751 US Sieve 75
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- Silt Fence (SF)
- Silt fences are used to prevent sediment carried by sheet flow from leaving the construction site by slowing storm water runoff and allowing settlement of soil particles. Areas directly upstream of silt fences are often prone to flooding due to the reduced flow rate through the silt fence, therefore special consideration should be given to fence placement. Silt fence shall not be installed in areas of concentrated flow such as swales or streams.
- All silt fence shall be installed in 2 parrallel rows, 2 feet apart.
- The 2 foot zone between silt fence rows shall be covered in 6 inches of loose straw.
- Sediment buildup at silt fences shall be removed when sediment reaches one-half of the height of the fabric.
- Fence posts shall be “T” shaped with minimum weight of 1.3 lbs/ft.
- Silt fence- type A
- Type A silt fence is the standard silt fence utilized by Auburn University.
- Type A is used in locations of high flow and is supported by wire reinforcement.
- Type A silt fence is reinforced with either galvanized steel:
- 12 gauge “hog wire” with small openings oriented at the base of the silt fence.
- 14 gauge 4”x4” wire mesh size, W1.4/1.4
- Silt fence- Type B is not used on campus
- Silt fence- Type C is not used on campus
- Placement of silt fence
- Silt Fence Material Requirements
- Temporary Fencing
- In general, all work areas shall be fenced. It is acceptable to use yellow caution tape in the event of emergencies and other unforeseen events. However, the tape should be replaced with orange flexible fencing if the work continues beyond 1 day. “Cattle-gates” are the preferred temporary fencing method and shall be used whenever and wherever possible, and for all events lasting longer than 3 days.
Last Updated:
Mar 05, 2013