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Chapter 11
Appendix
11.30. Risk, Compliance Issues, and Management Examples for Highway-Generated Waste - Oregon DOT

Table 29 : Risk, Compliance Issues, and Management Examples for Highway-Generated Waste - Oregon DOT

Waste

Toxicity/Risk

Compliance issues

Management Examples

Vactor Waste • Catchment Cleanout • Sediment Ponds • Bridge Culverts

High ( in urban areas ) . Typically the most contaminated roadwaste. Hydrocarbons and metals are common. Historical pollutants can be present. Low to High Depending on factors such as ADT, land-use, maintenance schedules, etc. Low ( if content of silt or fine soils is low ) .

Vactor waste must be separated into liquids and solids prior to disposal. Each waste must be disposed of separately. Many waste disposal rules apply. ODOT Environmental and DEQ can offer guidance. Even free of toxins, litter, and trash, vactor waste requires proper placing and erosion control.

• Develop alternative disposal options such as bioremediation or composting. • Pursue alternative decanting techniques ( retrofit sewerage manholes for liquid field disposal, treat vactor slurries with flocculent, etc. ) . • Partner with other agencies and share waste disposal facilities. • Construct ODOT decant facilities that separate vactor waste into liquids and solids. Landfill solids and dispose liquids to sewer.

Sweepings • Winter Sand

Low to High

Litter and sharps will be obvious. Hydrocarbons and metals are a concern. Urban sweepings usually test high in toxin levels. Low ( with quick pick up ) . Less time on roadway reduces litter and toxins.

Similar to vactor solids in risk and environmental concerns. Testing may be needed to determine toxin levels. Litter and trash must be disposed of at permitted waste facilities.

• Test, characterize, and sort for reuse. • Develop re-use options: compost, shoulder repair, fill, concrete, etc. ( remove trash by screening ) . • Develop and permit disposal sites ( partnering ) . • Thermal treatment ( incinerator ) . • Landfill.

Ditching Spoils

Low to Medium Generally risk is low but urban ditchings have tested positive for toxins ( hydrocarbons, metals, historical pollutants, chemical dumping, etc ) .

Storage sites must be suitable ( protect wetlands and streams ) . Clean soil is a pollutant if it is not contained ( erosion control ) .

• Use as fill material in appropriate locations. • Partner in give-away programs if material is suitable ( agriculture, construction, etc. ) . • Develop and permit disposal sites.

Landscape Cuttings

Low Nitrogen, bacteria, and other pollutants associated with the break down of organic material can be considered toxic pollutants.

Landscape debris must be disposed at permitted facilities. Composting is allowed but may require a permit. Odor, vector control, and public perception are concerns.

• Keep landscape debris separate from other waste and dispose appropriately. • Composting. • Burning ( only allowed at limited locations ) . • Chipping/Mulching.

Construction Soils and Slide Debris

Low Toxins can sometimes be a concern ( fuel spills, septic waste, excessive vegetation, etc. )

Similar to Ditching Spoils in risks and concerns. Storage sites must be suitable. Material must be contained.

• Use as fill or construction material if appropriate ( rock fall or sound berms, general fill, etc. ) . • Develop give-away programs with partners. • Develop and permit disposal sites.

 

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Table of Contents
 
Chapter 11
Appendix
11.1 Florida DOT Environmental Policy 11-1
11.2 Kentucky Transportation Cabinet Environmental Policy 11-1
11.3 Maine Dot Environmental Policy 11-2
11.4 North Carolina DOT Environmental Stewardship Policy 11-3
11.5 PennDOT’s Green Plan Policy Statement 11-3
11.6 Washington State Dot Environmental Policy 11-4
11.7 New South Wales Roads and Traffic Authority Environmental Policy 11-4
11.8 Texas Environmental Commitment Checklist 11-5
11.9 Maine DOT Environmental and Safety Auditing Policy and Procedure 11-11
11.10 Maine DOT Corrective Action Request Form 11-14
11.11 Mass Highway Compliance Tracking Methods 11-15
11.12 Mass Highway Compliance Tracking Roles and Responsibilities 11-16
11.13 Mass Highway Self-Audit Procedure 11-17
11.14 Mass Highway Facility Self-Audit Checklist 11-18
11.15 Mass Highway Environmental Roles & Responsibilities 11-20
11.16 Mass Highway Environmental Section EMS Roles and Responsibilities 11-20
11.17 Mass Highway Operations Division EMS Roles and Responsibilities 11-22
11.18 Mass Highway District EMS Roles and Responsibilities 11-23
11.19 Mass Highway Training Expectations By Role 11-24
11.20 Mass Highway Environmental Training Program Roles and Responsibilities 11-25
11.21 PennDOT District 10 SEMP Responsibility Table 11-26
11.22 PennDOT District 10 SEMP Training Table 11-28
11.23 NYSDOT Construction/Environmental Training Schedule 11-29
11.24 Environmental Checklist for MoDOT Facilities 11-30
11.25 PennDOT Stockpile Quality Assurance Responsibilities 11-33
11.26 PennDOT 15-Minute Stockpile Walkaround 11-34
11.27 PennDOT Stockpile Snapshot 11-34
11.28 PennDOT Maintenance Stockpile Activity Protocol 11-35
11.29 PennDOT Post-Storm Salt Management Tracking Responsibilities 11-41
11.30 Risk, Compliance Issues, and Management Examples for Highway-Generated Waste - Oregon DOT 11-42
11.31 NYSDOT-DEC Deer Carcass Composting – Practice Guidelines 11-43
11.32 NYSDOT’s Draft Metric for Assessing Performance of Integrated Vegetation Management on ROW 11-47
11.33 NCDOT Roadside Vegetation Management Guidelines in Marked Areas 11-50
11.34 Invasive Species Coordination and Control DOT Resources
   
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