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FINAL
HAZARDOUS WASTE MANAGEMENT PLAN
UNITED STATES ARMY AVIATION CENTER OF EXCELLENCE
FORT RUCKER, ALABAMA
Prepared for: U.S. Army Corps of Engineers
Mobile District Mobile, Alabama
Prepared by Trinity Analysis & Development Corp.
1002 North Eglin Parkway Shalimar, FL 32579
(850) 613-6800
September 2016
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TABLE OF CONTENTS
i
TABLE OF CONTENTS Contact List .................................................................................................................. xi Section 1 Introduction ............................................................................................. 1-1
1.1 Purpose and Objective .............................................................................. 1-1
1.2 Applicability ............................................................................................... 1-1
1.3 Implementation ......................................................................................... 1-2
1.4 Fort Rucker Environmental Management System ..................................... 1-2
1.4.1 Plan Review ................................................................................... 1-2
1.4.2 Revision Log .................................................................................. 1-3
Section 2 Installation and Regulatory Overview ................................................... 2-1
2.1 General ..................................................................................................... 2-1
2.2 Regulatory Authority ................................................................................. 2-7
2.2.1 Federal Regulations ....................................................................... 2-7
2.2.2 State Regulations .......................................................................... 2-7
2.2.3 Army Regulations .......................................................................... 2-8
2.2.4 Fort Rucker Policies ....................................................................... 2-9
2.3 RCRA Generator Status ......................................................................... 2-10
2.4 EPA Identification (ID) Number ............................................................... 2-12
2.5 Hazardous Waste Accumulation Sites (HWAS) ...................................... 2-12
2.6 General Hazardous Waste Training Requirements ................................. 2-13
Section 3 Responsibilities ...................................................................................... 3-1
3.1 General ..................................................................................................... 3-1
3.2 Garrison Commander ............................................................................... 3-1
3.3 Environmental Quality Control Committee (EQCC) .................................. 3-2
3.4 Commanders, Directors, and Supervisors (Military, Civilian, and
Contractors) ....................................................................................................... 3-2
3.5 Hazardous Waste Satellite Accumulation Point (HWSAP) Managers ....... 3-4
3.6 90-HWAS Managers ................................................................................. 3-6
3.7 Personnel Working With Hazardous Wastes ............................................ 3-8
3.8 EO and EPOC ........................................................................................... 3-8
3.9 Director of Public Works ........................................................................... 3-9
TABLE OF CONTENTS
ii
3.10 DPW-ENRD ........................................................................................... 3-9
3.11 Defense Logistics Agency Disposition Services (DLADS) Eglin .......... 3-11
3.12 Public Affairs Office (PAO) .................................................................. 3-11
3.13 Logistics Readiness Center (LRC) ...................................................... 3-12
3.14 Civilian Personnel Advisory Center (CPAC) ........................................ 3-12
Section 4 Hazardous Waste Identification and Classification ............................. 4-1
4.1 General ..................................................................................................... 4-1
4.2 Exemptions from Hazardous Waste Definition .......................................... 4-1
4.3 Listed Wastes ........................................................................................... 4-2
4.4 Characteristic Wastes ............................................................................... 4-3
4.5 Fort Rucker Waste Identification Requirements ........................................ 4-4
Section 5 Hazardous Waste Satellite Accumulation Points ................................ 5-1
5.1 General ..................................................................................................... 5-1
5.2 HWSAP Managers .................................................................................... 5-1
5.3 Waste Accumulation Quantities ................................................................ 5-2
5.4 Container Management Requirements ..................................................... 5-3
5.4.1 Compatibility .................................................................................. 5-3
5.4.2 General Requirements ................................................................... 5-3
5.4.3 Liquid Waste Container Requirements .......................................... 5-4
5.4.4 Labels and Signs ........................................................................... 5-4
5.4.5 Interim Container Management ..................................................... 5-4
5.5 Security ..................................................................................................... 5-4
5.6 Spill Prevention and Response ................................................................. 5-5
5.7 Inspections ................................................................................................ 5-6
5.8 Training ..................................................................................................... 5-7
5.9 Recordkeeping .......................................................................................... 5-8
5.9.1 Records that must be kept in the HWSAP ..................................... 5-8
5.9.2 Records that may be kept in a separate work area ........................ 5-8
Section 6 Hazardous Waste Accumulation Sites .................................................. 6-1
6.1 Hazardous Waste Accumulation Sites ...................................................... 6-1
6.2 Waste Accumulation ................................................................................. 6-1
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iii
6.3 Signage ..................................................................................................... 6-2
6.4 Facility Specifications ................................................................................ 6-2
6.5 Container Management Requirements ..................................................... 6-3
6.5.1 Container Stacking ........................................................................ 6-3
6.5.2 Container Specifications ................................................................ 6-3
6.5.3 Waste and Container Compatibility ................................................ 6-4
6.5.4 Damaged Containers ..................................................................... 6-5
6.5.5 Container Labeling ......................................................................... 6-5
6.6 Security ..................................................................................................... 6-6
6.7 Spill Prevention and Response ................................................................. 6-6
6.8 Inspections ................................................................................................ 6-7
6.9 Training ..................................................................................................... 6-7
6.10 Recordkeeping ...................................................................................... 6-8
6.10.1 Records that must be kept in the 90-HWAS ................................ 6-8
6.10.2 Records that may be kept in a separate work area ...................... 6-9
Section 7 Hazardous Waste Disposal Procedures ............................................... 7-1
7.1 General ..................................................................................................... 7-1
7.2 Hazardous Material Reuse Evaluation ...................................................... 7-1
7.3 Preparation for Disposal and Packaging ................................................... 7-1
7.4 Hazardous Waste Turn In Procedures ...................................................... 7-2
7.5 Waste Profiles ........................................................................................... 7-2
7.6 Hazardous Waste Marking and Labeling Requirements ........................... 7-3
7.6.1 General Requirements ................................................................... 7-3
7.6.2 Marking .......................................................................................... 7-4
7.6.3 Labeling ......................................................................................... 7-5
7.7 Turn-In Documentation ............................................................................. 7-5
7.8 Transportation of Hazardous Waste ......................................................... 7-6
7.9 Manifests................................................................................................... 7-7
7.10 Exception Reporting .............................................................................. 7-8
7.11 Recordkeeping ...................................................................................... 7-9
7.12 Hazardous Waste Reporting ............................................................... 7-10
TABLE OF CONTENTS
iv
Section 8 Hazardous Waste Analysis Plan ........................................................... 8-1
8.1 General ..................................................................................................... 8-1
8.2 Analysis Cost ............................................................................................ 8-1
8.3 Chain-of-Custody Forms ........................................................................... 8-1
8.4 Results ...................................................................................................... 8-2
8.5 Characterization Frequency ...................................................................... 8-2
8.6 Unknown Wastes ...................................................................................... 8-2
8.7 Land Disposal Restrictions........................................................................ 8-3
Section 9 Hazardous Waste Minimization ............................................................. 9-1
9.1 Pollution Prevention Plan .......................................................................... 9-1
9.2 Hazardous Materials ................................................................................. 9-2
9.3 EMS Objectives and Targets .................................................................... 9-2
Section 10 Installation Waste Stream Summary ................................................... 10-1
10.1 General ............................................................................................... 10-1
10.2 Hazardous Waste ................................................................................ 10-1
10.3 Non-Hazardous Wastes ...................................................................... 10-2
10.4 Universal Waste .................................................................................. 10-2
10.5 Prohibited Items .................................................................................. 10-3
10.6 Polychlorinated Biphenyls ................................................................... 10-3
10.7 Regulated Medical Waste (RMW) ....................................................... 10-4
Section 11 Waste Stream Management ................................................................. 11-1
11.1 Absorbent Materials ............................................................................ 11-1
11.1.1 Continued Use Absorbents ........................................................ 11-1
11.1.2 Disposable Absorbents .............................................................. 11-2
11.1.3 Sweeping Compound ................................................................ 11-2
11.2 Adhesives ............................................................................................ 11-3
11.3 Aerosol Containers .............................................................................. 11-3
11.4 Antifreeze ............................................................................................ 11-3
11.5 Asbestos ............................................................................................. 11-4
11.6 Asphalt and Related Wastes ............................................................... 11-4
11.7 Batteries .............................................................................................. 11-4
TABLE OF CONTENTS
v
11.7.1 General Requirements ............................................................... 11-4
11.7.2 Small Rechargeable Batteries ................................................... 11-6
11.7.3 Lead Acid Batteries .................................................................... 11-6
11.8 Battery Fluid ........................................................................................ 11-7
11.9 Blast Media.......................................................................................... 11-7
11.10 Boiler Treatment .............................................................................. 11-8
11.11 Corrosion Prevention and Removal ................................................. 11-8
11.12 Cylinders .......................................................................................... 11-8
11.13 Empty Containers............................................................................. 11-9
11.14 Fuel ................................................................................................ 11-10
11.15 Fuel Filters ..................................................................................... 11-10
11.16 Grease and Related Items ............................................................. 11-11
11.17 Image Intensifier Tubes .................................................................. 11-11
11.18 Insect Repellant ............................................................................. 11-11
11.19 Medical Activities ........................................................................... 11-11
11.20 Mercury-Containing Lamps ............................................................ 11-12
11.21 Mercury-Containing Equipment ...................................................... 11-12
11.22 Military Munitions ........................................................................... 11-13
11.23 Nuclear, Biological, Chemical (NBC) Items .................................... 11-13
11.24 Paint Related Items ........................................................................ 11-13
11.24.1 Latex Paint ............................................................................. 11-13
11.24.2 Hazardous Waste Paint and Thinner ..................................... 11-14
11.24.3 Paint Containers .................................................................... 11-14
11.24.4 Paint Solids ............................................................................ 11-14
11.25 Parts Washer Solvent and Filters ................................................... 11-14
11.26 Pesticides, Herbicides, and Rodenticides ...................................... 11-15
11.27 Photo Processing Chemicals ......................................................... 11-16
11.28 Plating Shop Wastes ...................................................................... 11-16
11.29 Polychlorinated Biphenyls .............................................................. 11-16
11.30 Process Particulates ...................................................................... 11-17
11.31 Ration Heaters ............................................................................... 11-18
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vi
11.32 Scrap Items .................................................................................... 11-18
11.32.1 Scrap Metal ............................................................................ 11-18
11.32.2 Items Requiring Special Handling .......................................... 11-18
11.33 Solder ............................................................................................. 11-19
11.34 Toner .............................................................................................. 11-19
11.35 Used Oil ......................................................................................... 11-19
11.36 Used Oil Filters .............................................................................. 11-20
11.37 Washrack Sand/Soil ....................................................................... 11-20
11.38 Weapons Cleaning Materials ......................................................... 11-20
11.39 X-Ray Rinse Water ........................................................................ 11-21
11.40 Zyglo Rinsate ................................................................................. 11-21
Section 12 Spill Response Procedures ................................................................. 12-1
12.1 General ............................................................................................... 12-1
12.2 Spill Response and Emergency Procedures ....................................... 12-1
12.3 Spill Contingency Plans ....................................................................... 12-2
12.4 Spill Contingency Training ................................................................... 12-3
12.5 Spill Contingency Supplies .................................................................. 12-3
12.6 Spill Reporting ..................................................................................... 12-3
LIST OF TABLES
Table 4-1 Maximum Concentration of Contaminants for the Toxicity Characteristic .... 4-6
LIST OF FIGURES Figure 2-1 Site Location Map ....................................................................................... 2-3
Figure 2-2 Installation Map ........................................................................................... 2-5
Figure 2-3 Hazardous Waste and Universal Waste Disposed per Year ..................... 2-11
TABLE OF CONTENTS
vii
LIST OF APPENDICES Appendix A Waste Disposal Data CY10-CY15
Appendix B USAACE Form 2735, Hazardous Waste Job Description and Training
Record
Appendix C USAACE Form 2729, EO/EPOC Appointment Memo
Appendix D USAACE Form 2733, HWSAP and 90-Day HWAS Manager Appointment
Memo
Appendix E Inspection Forms (USAACE Form 2725, HWSAP Inspection Checklist;
USAACE Form 2726, 90-HWAS Inspection Log; USAACE Form 2711,
SPCC Plan Container Inspection Form; USAACE Form 2717,
Environmental Compliance Inspection Checklist)
Appendix F ADEM Letters and Guidance
Appendix G USAACE Form 2716, Secondary Containment Drainage Activity Log
Appendix H DD Form 1348-1A, Issue Release/Receipt Document
Appendix I 49 CFR 172.400 Excerpt
Appendix J EMS-WI-SW010, Contractor Hazardous Waste Management
Appendix K EMS-WI-SW001, Waste Turn-In Procedure
Appendix L Hazardous Waste Profile
Appendix M Container Labels
Appendix N USAACE Form 2730, Hazardous Material Authorization Request
Appendix O EMS-WI-SW009, Absorbent Continued Use Program
Appendix P USAACE Form 2732, Continued Use Absorbents Tracking Document
Appendix Q EMS-WI-SW002, Used Battery Management
Appendix R EMS-WI-SW007, Management of Used Oil and Fuel Filters
Appendix S EMS-WI-SW003, Used Lamps Management
Appendix T USAACE Form 2719, Site Specific Spill Plan
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ABBREVIATIONS AND ACRONYMS
ix
LIST OF ABBREVIATIONS AND ACRONYMS
90-HWAS 90-Day Hazardous Waste Accumulation Site ADEM Alabama Department of Environmental Management AMSS Aviation Maintenance Support Shop AR Army Regulation ASP Ammunition Supply Point CARC Chemical Agent Resistant Coating CFR Code of Federal Regulations CPAC Civilian Personnel Advisory Center CY Calendar Year DA Department of the Army DLADS Defense Logistics Agency Disposition Services DoD Department of Defense DPW Directorate of Public Works DPW-ENRD Directorate of Public Works, Environmental and Natural Resources
Division DS2 Decontamination Solution Number 2 EESOH-MIS Enterprise Environmental, Safety, and Occupational Health
Management Information System EMS Environmental Management System EMSMR Environmental Management System Management Representative EO Environmental Officer EPA Environmental Protection Agency EPOC Environmental Point of Contact EQCC Environmental Quality Control Committee FIFRA Federal Insecticide, Fungicide, and Rodenticide Act FRH Flameless Ration Heaters GAA Grease, Automotive and Aviation HID High Intensity Discharge HM Hazardous Material HM/HW Hazardous Material/Hazardous Waste HMCC Hazardous Material Control Center HMMP Hazardous Material Management Program HQDA Headquarters, Department of the Army HW Hazardous Waste HWAS Hazardous Waste Accumulation Site
ABBREVIATIONS AND ACRONYMS
x
HWMP Hazardous Waste Management Plan HWSAP Hazardous Waste Satellite Accumulation Point ID Identification ISCP Installation Spill Contingency Plan LBP Lead-Based Paint LDR Land Disposal Restrictions LiSO2 Lithium Sulfur Dioxide LQG Large Quantity Generator LRC Logistics Readiness Center MOGAS Motor Gasoline MRE Meal Ready-to-Eat MRIP Munitions Rule Implementation Policy NBC Nuclear, Biological, and Chemical NDI Non-Destructive Investigation NiCd Nickel-Cadmium NiMH Nickel Metal Hydride NOV Notice of Violation NRC National Response Center P2 Pollution Prevention PAO Public Affairs Office PCB Polychlorinated Biphenyls POC Point of Contact POL Petroleum, Oil, and Lubricants PPE Personal Protective Equipment RCRA Resource Conservation and Recovery Act RMW Regulated Medical Waste SDS Safety Data Sheet SJA Staff Judge Advocate SOP Standard Operating Procedure SPCC Spill Prevention, Control and Countermeasures STB Super Tropical Bleach TSCA Toxic Substances Control Act TSD Treatment, Storage and Disposal UCMJ Uniform Code of Military Justice USAACE U.S. Army Aviation Center of Excellence WMM Waste Military Munitions
CONTACT LIST
xi
Contact List
Title Phone #
Chief, Environmental and Natural Resources Division 334-255-1659
Hazardous Waste Program Manager 334-255-1024
Solid Waste Program 334-255-1656
Recycling Manager 334-255-1658
Hazardous Waste Turn-In on Main Post Thursday 0900-1130 or by appointment (Office Hours 0730 to 1600 hrs.)
334-598-1311
DLADS Fort Rucker Office 334-255-2939
DLADS Representative (Eglin AFB) Comm. 850-882-8076/850-882-2824 or
DSN 872-8076/872-2824
Fire Department (for emergency, dial 911) 334-255-0044
Alabama Department of Environmental Management (ADEM) 1400 Coliseum Boulevard Montgomery, Alabama 36110-2400
334-271-7700
xii
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SECTION ONE Introduction
1-1
Section 1 Introduction
1.1 PURPOSE AND OBJECTIVE
The United States Army is committed to proper handling of the hazardous wastes that
are generated on its installations. The primary objective of this document is to provide a
plan that gives personnel working with hazardous waste the essential tools for effective
management. The purpose of this plan is to identify and establish the requirements for
the accumulation, storage, handling, and disposal of hazardous waste on Fort Rucker
from the point of generation to the point of disposal.
This plan was developed in accordance with Army Regulation (AR) 200-1, Environmental
Protection and Enhancement; the Alabama Department of Environmental Management
(ADEM) Administrative Code; and the Resource Conservation and Recovery Act (RCRA),
as amended. In the event that any of the provisions contained in this plan are superseded
or otherwise modified by changes to the Code of Federal Regulations (CFR) or the ADEM
Administrative Code, the CFR and ADEM Administrative Code will take precedence over
this plan.
This document implements the requirements of AR 200-1, Chapter 10-1 and provides
installation personnel with specific procedures and responsibilities to manage hazardous
wastes consistent with federal, state and local laws and regulations. The Hazardous
Waste Management Plan (HWMP) serves as documentation for regulatory authorities
that such a program is in place.
The HWMP documents personnel and procedures to ensure each step in the "cradle-to-
grave" management of hazardous wastes is carried out in a consistent manner and in
accordance with regulatory requirements. Procedures are either referenced or included
in this HWMP, as necessary, to provide documented hazardous waste management
instructions, from the time of waste generation until it is transported offsite for reuse or
disposal.
1.2 APPLICABILITY
The HWMP is intended to be comprehensive, covering all operations involving hazardous
waste, including all activities and tenants that generate or otherwise manage hazardous
waste, including those activities located at facilities outside the contiguous boundary of
SECTION ONE Introduction
1-2
Fort Rucker. The requirements of this document are applicable to all military, civilian and
contract personnel at Fort Rucker, including commanders and directors.
1.3 IMPLEMENTATION
Implementation of a comprehensive hazardous waste management program mandated
by RCRA requires maximum cooperation of all activities on Fort Rucker. It is the
responsibility of the Garrison Commander to ensure compliance with all RCRA
requirements for Fort Rucker and to notify and report to Environmental Protection Agency
(EPA) or ADEM, as required, for all installation activities, including tenant activities. The
individual installation organizations (generating activities) are accountable for conducting
their activities in accordance with this plan. Each generating organization will ensure
compliance with RCRA regulations at the facility.
1.4 FORT RUCKER ENVIRONMENTAL MANAGEMENT SYSTEM
Hazardous waste is one of the significant aspects identified within the Fort Rucker
Environmental Management System (EMS). This HWMP serves as an operational control
as specified in EMS-P016, Operational Controls Procedure. This document is a controlled
document with the official version maintained on the Sustainable Fort Rucker website
(www.fortrucker-env.com). All forms and work instructions referenced within this
document are also controlled documents. Forms and work instructions are included in the
appendices for reference only; the official versions of all documents are maintained on
the Sustainable Fort Rucker website. The following tables should be used to document
plan review and amendments.
1.4.1 Plan Review This plan will be reviewed at least annually and when a process change occurs. The
review will be documented in the following table.
Date Review Completed Signature of Person Performing Review Comments
SECTION ONE Introduction
1-3
1.4.2 Revision Log Revisions made to the plan, including the date of the revision, the section of the plan
being revised, the reason for the change, and the signature of the person making the
change will be documented in the following table.
Date of Change
Page Numbers/ Section
Signature of Person Performing Review Reason for Change
SECTION ONE Introduction
1-4
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SECTION TWO Installation and Regulatory Overview
2-1
Section 2 Installation and Regulatory Overview
2.1 GENERAL
Fort Rucker is located in southeast Alabama, 20 miles northwest of Dothan, Alabama. It
is surrounded by the towns of Daleville on the south, Enterprise on the west, and Ozark
on the east (Figure 2-1). Fort Rucker is positioned in a topographical area of southeastern
Alabama that consists of moderately rolling lands with elevations ranging from 200 to 300
feet above mean sea level.
The installation spans over two Alabama counties, Dale and Coffee, and covers a total of
62,321 acres, which is composed of 57,885 acres at the main post, 1,297 acres at Cairns
Army Airfield, 247 acres at Shell Army Heliport, 1,220 acres at small stagefields within a
five-county area, and 1,672 acres of leases and easements. The airfields, heliports, and
stagefields are listed below and depicted in Figure 2-2. The various fields are indicated
with only the name and not the type of field when they are discussed within this document.
• Allen Stagefield
• Brown Stagefield
• Cairns Army Airfield
• Ech Stagefield
• Goldberg Stagefield
• Guthrie Airfield (not active)
• Hanchey Army Heliport
• Hatch Stagefield
• Highbluff Stagefield
• Highfalls Stagefield
• Hooper Stagefield
• Hunt Stagefield
• Knox Army Heliport
• Louisville Stagefield
• Lowe Army Heliport
• Lucas Stagefield
• Molinelli Stagefield
SECTION TWO Installation and Regulatory Overview
2-2
• Runkle Stagefield
• Shell Army Heliport
• Skelly Stagefield
• Stinson Stagefield
• Tabernacle Stagefield
• Tac-X Stagefield
• Toth Stagefield
• Wolfpit Tactical Site
The primary missions of Fort Rucker are pilot training, aircraft maintenance, and air traffic
control training with emphasis on rotary-wing aircraft. Hazardous wastes are generated
primarily as the result of maintenance of Army equipment and property as well as from
expired hazardous materials. These wastes are generated and managed at numerous
locations across Fort Rucker.
SECTION TWO Installation and Regulatory Overview
2-3
Figure 2-1 Site Location Map
SECTION TWO Installation and Regulatory Overview
2-4
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SECTION TWO Installation and Regulatory Overview
2-5
Figure 2-2 Installation Map
SECTION TWO Installation and Regulatory Overview
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SECTION TWO Installation and Regulatory Overview
2-7
2.2 REGULATORY AUTHORITY
2.2.1 Federal Regulations RCRA is the principal Federal legislation governing the management of solid and
hazardous waste. The EPA has established regulations under RCRA which govern
hazardous waste generation, storage, transportation, and disposal under Title 40 of the
CFR Parts 260 through 299.
• Part 260 provides general guidance for the use of the regulations and sets forth
provisions, which are applicable to all parts.
• Part 261 identifies and lists various wastes considered by EPA to be hazardous.
This part establishes the criteria by which wastes are characterized as hazardous.
• Part 262 establishes standards applicable to generators of hazardous waste,
including requirements for reporting and manifesting of hazardous waste
shipments.
• Part 263 establishes standards for transporters of hazardous wastes including
manifesting and recordkeeping.
• Part 264 establishes standards for owners and operators of hazardous waste
treatment, storage, and disposal (TSD) facilities.
• Part 265 establishes interim status standards for owners and operators of
hazardous waste TSD facilities. These are the standards with which existing
facilities must comply if they are to remain in operation until EPA takes final action
on their permit applications.
• Part 268 provides land disposal restrictions (LDR).
• Part 273 provides standards for Universal Waste Management.
• Part 279 provides standards for the management of used oil.
2.2.2 State Regulations On December 22, 1987, the State of Alabama was granted final authorization from the
EPA to operate its own hazardous waste management program. The authorization,
however, is subject to the authority retained by EPA in accordance with the Hazardous
and Solid Waste Amendments (HSWA) of 1984. Generators, transporters, and
owners/operators of hazardous waste TSD facilities in Alabama are now subject to the
SECTION TWO Installation and Regulatory Overview
2-8
Alabama Hazardous Waste Management Rules in lieu of the Federal regulations adopted
by the EPA.
ADEM has been designated the lead agency in developing and administering the
hazardous waste management program in Alabama.
The Alabama Hazardous Waste Management Rules are contained in the ADEM
Administrative Code, Land Division - Hazardous Waste Program - Division 14. The State
of Alabama has essentially adopted the Federal hazardous waste regulations. Some of
Alabama’s requirements are more stringent than the federal requirements. Any
management requirements that are stricter than federal requirements are specified in the
appropriate section of this plan. In Alabama, any generator (including small quantity
generators who are partially exempt under RCRA) may be required to obtain approval
before transporting, treating, or disposing of certain types of hazardous waste. The
following sections are included in the ADEM Administrative Code:
• Chapter 335-14-1 - Hazardous Waste Management System: General
• Chapter 335-14-2 - Identification and Listing of Hazardous Waste
• Chapter 335-14-3 - Standards Applicable to Generators of Hazardous Waste
• Chapter 335-14-4 - Standards Applicable to Transporters of Hazardous Waste
• Chapter 335-14-5 - Standards for Owners and Operators of Hazardous Waste
Treatment, Storage and Disposal Facilities
• Chapter 335-14-6 - Interim Status Standards for Owners and Operators of
Hazardous Waste Treatment, Storage and Disposal Facilities
• Chapter 335-14-7 - Standards for the Management of Specific Hazardous Wastes
and Specific Types of Hazardous Waste Management Facilities
• Chapter 335-14-8 - Permit Program
• Chapter 335-14-9 - Land Disposal Restrictions
• Chapter 335-14-11 - Standards for Universal Waste Management
• Chapter 335-14-17 - Standards for the Management of Used Oil
2.2.3 Army Regulations The Army is committed to environmental stewardship in all actions as an integral part of
the Army mission. Department of Defense (DOD) installations and personnel are required
SECTION TWO Installation and Regulatory Overview
2-9
to comply with all federal, state, and local laws, as well as Army requirements, designed
to protect human health and the environment. Pursuant to this requirement, the
Department of the Army (DA) has developed AR 200-1, Environmental Protection and
Enhancement, which prescribes responsibilities, policies, and procedures to preserve,
protect, and restore the quality of the environment. This regulation is to be implemented
in a number of areas, including hazardous waste management. The procedures in
Chapter 10 of AR 200-1 incorporate all applicable regulatory requirements for hazardous
waste management, and specify implementation of local procedures and responsibilities
for execution of the hazardous waste management program. Chapter 10, Waste
Management, further defines the policy for managing hazardous and solid wastes.
Related policy guidance on solid waste may be found in AR 420-1, Army Facilities
Management. Specifically, Fort Rucker should ensure that waste accumulation, storage,
or transfer facilities are designed and constructed to prevent releases to the environment.
This document includes the elements of a HWMP required by AR 200-1:
Chapter 10-1.d.(3) Develop and implement a hazardous waste management plan
(HWMP) or other comparable document appropriate to the size and complexity of the
operation. The HWMP (or other comparable document) should include, at a minimum,
written procedures for all aspects of hazardous waste management, to include the
identification, storage, and transporting of HW; training of personnel; tracking
manifests; and maintaining required records.
2.2.4 Fort Rucker Policies Regulatory Compliance
It is an installation policy that any command, activity, tenant, organization, or contractor
at Fort Rucker that generates or otherwise manages hazardous waste, is subject to and
shall comply with all applicable federal, state, local, Army and installation requirements.
The Directorate of Public Works, Environmental and Natural Resources Division (DPW-
ENRD) is responsible for administering the Fort Rucker HWMP. Any person found to be
violating the provisions of any of these requirements is subject to appropriate disciplinary
measures. In the absence of appropriate regulatory guidelines, hazardous waste shall be
SECTION TWO Installation and Regulatory Overview
2-10
managed in a manner that minimizes adverse effects to human health and the
environment.
Standard Operating Procedures
Standard operating procedures (SOPs) for hazardous waste - including but not limited to
hazardous waste accumulation, auditing/inspection, storage, and turn-in procedures -
shall be implemented by all activities on the installation that generate hazardous waste.
Current SOPs for activities that generate hazardous waste at Fort Rucker are included in
the EMS Master Document List as Work Instructions. The EMS Master Document List is
available on the Sustainable Fort Rucker website.
Waste Minimization
Potential hazardous wastes will be recycled and reused to the maximum extent
practicable at Fort Rucker. Hazardous wastes, which are not economically recoverable,
shall be disposed in a way that will prevent or minimize pollution of the environment and
in compliance with federal, state, and local hazardous waste regulations. Emphasis will
be placed on source reduction and materials substitution methods.
Army military, civil works activities, and tenants are required to establish procedures and
responsibilities for the execution of the waste management program which emphasizes
pollution prevention, chain of command, and individual responsibility to achieve
compliance and minimize waste generation, treatment, and disposal through pollution
prevention actions.
2.3 RCRA GENERATOR STATUS
Waste is generated as a result of many types of installation activities, including vehicle
and aircraft maintenance; military training activities; fuel and hazardous material spills;
medical operations; battery shops; and construction projects. Waste is generated by
military, civilian, and contractor personnel working on Fort Rucker. Appendix A contains
waste generation data for the largest waste streams at Fort Rucker.
Fort Rucker is a large quantity generator, generating 17 tons of hazardous waste in CY15.
Figure 2-3 shows the quantities of hazardous waste and universal waste disposed from
CY10 through CY15.
SECTION TWO Installation and Regulatory Overview
2-11
Figure 2-3 Hazardous Waste and Universal Waste Disposed per Year
0
10
20
30
40
50
60
70
CY10 CY11 CY12 CY13 CY14 CY15
Haz
ardo
us W
aste
and
Uni
vers
al W
aste
Dis
spos
ed
(tons
)
Hazardous Waste
Universal Waste
SECTION TWO Installation and Regulatory Overview
2-12
2.4 EPA IDENTIFICATION (ID) NUMBER
Fort Rucker is a large quantity generator (e.g. greater than 1000 kg per month) of
hazardous waste. The Fort Rucker EPA/State identification (ID) number for generating
hazardous waste is AL6210020776.
Cairns Army Airfield is not contiguous to Fort Rucker and is a large quantity generator.
The EPA/State ID number for Cairns for generating hazardous waste is AL9210090040.
Additionally, Shell Army Heliport is not contiguous to Fort Rucker and is a small quantity
generator. The EPA/State ID number for Shell for generating hazardous waste is
AL2210090039.
2.5 HAZARDOUS WASTE ACCUMULATION SITES (HWAS)
Currently, Fort Rucker has five 90-day Hazardous Waste Accumulation Sites (90-HWAS).
If operational conditions require closure of one of the 90-HWAS, it will be closed in
accordance with ADEM Administrative Code Chapter 335-14-3-.03(5)(a)5. This section
requires compliance with the closure requirements of 335-14-3-.03 and the applicable
requirements of 335-14-6-.09(9), 335-14-6-.10(8), 335-14-6-.23(6), and 335-14-6-.30(3),
and the record keeping requirements of rules 335-14-3-.04(1)(c) and 335-14-3-.04(4).
These 90-HWAS are located as follows:
1. Building 1207
2. Near Building 1001
3. Near the Lowe Army Heliport washrack
4. Near the Hanchey Army Heliport washrack
5. At Cairns Field between Hangars 30103 and 30104
Additionally, Fort Rucker operates a 180-day HWAS at Shell Army Heliport. Shell Field is
a small quantity generator, and the HWAS is a 180-day site. Fort Rucker manages this
HWAS with the same practices as at a 90-HWAS. Any references to requirements for a
90-HWAS are also applicable to the accumulation site at Shell.
SECTION TWO Installation and Regulatory Overview
2-13
2.6 GENERAL HAZARDOUS WASTE TRAINING REQUIREMENTS
This section provides general information related to the level of training required by all
personnel who manage or supervise hazardous waste activities or handle hazardous
waste in the course of their employment duties. The training shall be implemented by all
Fort Rucker installation and tenant activities. Information about the overall training
program is included in EMS-P014, Competence Based Training.
Federal and state regulations require that all personnel managing or handling hazardous
waste must be trained, either through classroom instruction or on-the-job-training, to
respond to emergencies, protect the environment, and properly handle and dispose of
hazardous wastes. The regulatory requirements for training may be found in ADEM,
Division 14, 335-14-5-.02(7).
Facility personnel whose duties have a direct effect on hazardous waste management
and/or hazardous waste accumulation, whether by direct contact with the hazardous
waste or through hazardous waste management activities, must receive training. Each
person managing or handling hazardous waste must receive introductory and annual
update hazardous waste training corresponding with his/her responsibilities. The annual
update training must be completed within 365 days of the previous training.
The introductory training must be completed within six months of the date on which the
employee begins work in a position requiring such training. Employees must be
immediately and continuously supervised when performing hazardous waste duties until
such training is completed.
At a minimum, all supervisors and managers of hazardous waste activities will be trained
in installation-sponsored or off-site training courses that meet the established training
requirements of this plan. It is their responsibility to ensure that personnel working for
them are trained either in formal courses or in-house using on-the-job-training and "shop
level" training classes to meet the regulatory requirements.
Personnel responsible for shipping hazardous waste and signing hazardous waste
manifests must be trained in accordance with Department of Transportation (DOT) 49
SECTION TWO Installation and Regulatory Overview
2-14
CFR 172, Subpart H, which requires initial and recurrent training. Only personnel within
DPW-ENRD designated by the Garrison Commander are authorized to sign manifests.
Each organization will develop a program to train its hazardous waste handlers, using an
appropriate combination of the following:
• Installation-sponsored hazardous waste training courses
o DOD Hazardous Material / Hazardous Waste (HM/HW) Handler Course –
24-hour initial training / 8-hour refresher training annually
o Hazardous Waste Satellite Accumulation Point (HWSAP) Manager Course
– 2-hour training annually
o 90-HWAS Manager Course – 2-hour training annually
• Off-site hazardous waste training courses
• Organization level training such as shop talks, lectures, and guest lectures
• Reading and discussing installation and organization level hazardous waste
management plans, SOPs, and spill contingency plans
• On-the-job instruction in hazardous waste management procedures from a person
trained in those procedures
• Performance of hazardous waste management procedures under the direct
supervision of a person trained in those procedures
All instances of training must be documented using USAACE Form 2735, Hazardous
Waste Job Description and Training Record, contained in Appendix B or otherwise
approved by DPW-ENRD in writing. The training record must include:
• Name of Employee
• Job Title
• Job Description
• A written description of the type and amount of both introductory and continued
training that will be given to each person filling a position.
• Records that document that the training required has been given to, and completed
by, facility personnel.
SECTION TWO Installation and Regulatory Overview
2-15
A training record must be maintained on-site for every person in the organization requiring
hazardous waste training. Individual records of training are required by state and federal
regulations to be maintained for three years after an employee leaves employment at the
organization. Training records may be transferred with an employee if the employee is
transferred to another job at the facility.
SECTION TWO Installation and Regulatory Overview
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SECTION THREE Responsibilities
3-1
Section 3 Responsibilities
3.1 GENERAL
Environmental compliance is both a command and an individual responsibility.
Commanders and heads of activities at all levels on and around Fort Rucker are
responsible for compliance with this HWMP. Responsibilities for implementing this plan
are distributed throughout installation organizations that generate, accumulate, transport,
turn-in, monitor, or respond to incidents involving hazardous waste. Overall compliance
with federal, state, and local hazardous waste laws and Army regulations is the
responsibility of the installation commander through the Environmental Management
System (EMS). This section specifies the responsibilities of all installation activities and
personnel (military, civilian, and contractors) in generating and accumulating hazardous
waste.
3.2 GARRISON COMMANDER
a. Ensures that Fort Rucker is compliant with all applicable environmental laws and
regulations.
b. Programs and budgets for the necessary funds and personnel in order to execute
a hazardous waste program and comply with applicable state, federal, and Army
regulations.
c. Serves as the chairperson of the EQCC which meets quarterly to discuss and
oversee pertinent environmental issues.
d. Signs RCRA permit applications, compliance agreements, consent orders, and
responses to Notices of Violation (NOV) with the state and federal regulatory
officials, following review by the installation Staff Judge Advocate (SJA) and the
Directorate of Public Works (DPW).
e. Establishes an organizational structure to plan, execute and monitor hazardous
waste programs and waste minimization initiatives.
f. Delegates the preparation and signature of all shipping manifests required by
federal and state law for wastes to appropriately trained personnel within DPW.
SECTION THREE Responsibilities
3-2
3.3 ENVIRONMENTAL QUALITY CONTROL COMMITTEE (EQCC)
a. Provides the Garrison Commander with a regularly scheduled status report on
environmental issues and actions, including those involving hazardous wastes and
materials.
b. Provides a forum for dissemination of information and a forum for the principal
parties responsible for environmental and occupational health to introduce and
resolve environmental issues.
c. Increases the awareness and active participation at all organizational levels in
meeting all the laws and regulatory requirements.
d. Ensures that management of hazardous waste on the installation complies with
applicable portions of ADEM Administrative Code Division 14 and 40 CFR Parts
260-279.
e. Ensures all enforcement actions are resolved quickly.
3.4 COMMANDERS, DIRECTORS, AND SUPERVISORS (MILITARY, CIVILIAN, AND CONTRACTORS)
The commander/director of each major subordinate command, brigade, battalion,
directorate, tenant organization, and civilian contractor that handles hazardous
materials/waste will:
a. Appoint in writing military personnel, civilian or contractor supervisors as
Environmental Officer (EO) or Environmental Points of Contact (EPOC) using
USAACE Form 2729, Environmental Officer and EPOC Appointment Memo, a
copy of which is located in Appendix C. See the Fort Rucker Environmental Officer
Appointment and Training Plan and the Fort Rucker Environmental Officer Policy
for additional information. Both of these documents are available on the
Sustainable Fort Rucker website.
b. Appoint in writing military personnel, civilian or contactor supervisors as 90-HWAS
and/or HWSAP managers (whichever is appropriate) using USAACE Form 2733,
HWSAP and HWAS Manager Appointment Memo, for all activities within their area
of responsibility that generate, manage, accumulate, store, and/or transport
hazardous waste. A copy of this form is located in Appendix D.
SECTION THREE Responsibilities
3-3
c. Identify all hazardous waste handlers within areas of responsibility. Identify the
location of all HWSAP and 90-HWAS within their organization, and submit an
updated list to DPW-ENRD at least annually (prior to October 1 of each year).
Provide written notification to the DPW-ENRD Hazardous Waste Program
Manager if any changes to waste streams or accumulation areas occur between
list submissions. Any proposed change, including adding or removing
accumulation areas or waste streams, should be coordinated with DPW-ENRD
prior to implementation.
d. Set organization-level hazardous waste management policy and establish an
active hazardous waste management program in compliance with all pertinent
laws and regulations and the Fort Rucker HWMP.
e. Ensure waste profile information changes (e.g. change in chemicals used, change
in safety data sheets [SDS], etc.) are communicated to DPW-ENRD prior to waste
accumulation.
f. Ensure that all hazardous waste managers and handlers are trained in accordance
with this HWMP.
g. Ensure that all personnel who may be exposed to hazardous waste in the course
of their work are made aware of the hazards to which they are exposed as well as
the precautions required to protect both the environment and themselves in
operational areas.
h. Ensure that materials and supplies, including the necessary and proper fitting of
personal protective equipment (PPE) and emergency response supplies, are
provided for the proper management and handling of hazardous waste.
i. Ensure notices from state or federal environmental agencies, including
enforcement actions and NOVs, noncompliance or administrative orders or
compliance requests, are forwarded within 24-hours to the Garrison Commander
with a notification copy to their command. Ensure that appropriate action is taken
to address negligent and willful violations of federal and state hazardous waste
laws and regulations, to correct operational deficiencies, and to prevent
reoccurrence of violations.
SECTION THREE Responsibilities
3-4
j. Prepare a Site Specific Spill Plan as specified in Appendix A of the Installation Spill
Contingency Plan (ISCP), which includes a contingency plan, for the storage and
management of hazardous waste for each 90-HWAS and HWSAP.
k. Ensure that all hazardous waste handlers obtain the initial mandatory training
program described in Section 5.8 and 6.9 within 60 days, and complete the initial
training program within six months of the date of their employment in or assignment
to the waste handling position. Ensure that newly assigned personnel do not work
in unsupervised positions until they have completed the initial training program.
Further, they ensure that all hazardous waste handlers complete the required
refresher training on an annual basis.
l. Ensure that the training records are maintained and kept at or near the 90-HWAS.
The records should document that the hazardous waste handlers have completed
the training. Training records on employees must be maintained during the course
of their employment and retained for at least three years past the date the
employees last worked within the organization.
m. Become familiar with the installation hazardous waste minimization goals in
accordance with Section 10 of this plan and implement as appropriate or as
required.
n. Units, tenants, and activities generating hazardous waste are responsible for
estimating annual hazardous waste disposal costs and including in budget
forecast.
3.5 HAZARDOUS WASTE SATELLITE ACCUMULATION POINT (HWSAP) MANAGERS
a. Serve as points of contact regarding the implementation of their hazardous waste
management program responsibilities within the installation or tenant organization.
b. Ensure an up-to-date appointment letter using USAACE Form 2733, HWSAP and
HWAS Manager Appointment Memo, from their supervisor/commander is readily
available and that the letter has been submitted to DPW-ENRD prior to performing
hazardous waste management duties. A copy of this form is located in Appendix D.
c. Ensure that all hazardous waste is placed in a DPW-ENRD approved HWSAP.
SECTION THREE Responsibilities
3-5
d. Ensure the appropriate information and warning signs are posted at each HWSAP.
HWSAP signs should include the following information: Hazardous Waste Satellite
Accumulation Point, HWSAP Manager Name and his/her telephone number, along
with the Alternate HWSAP Manager name and telephone number.
e. Ensure that appropriate EPA markings are on the hazardous waste label or
container, and represent the waste within:
• The words "HAZARDOUS WASTE"
• Description of the contents
• EPA ID number
• EPA Waste Code(s)
• Accumulation Start Date if the container is full.
f. Advise the Hazardous Waste Program Manager of any changes in chemicals or
processes that may impact the appropriate EPA markings on the waste container.
g. Ensure that appropriate EPA markings are on universal waste labels or containers:
• The words "UNIVERSAL WASTE"
• The words “Used Lamps”, “Used Mercury Thermostats”, “Used Batteries”, or
“Waste Pesticides” (as appropriate)
• The accumulation start date, which is the date the first item is placed in the
container.
h. Ensure that accurate descriptions including the weights (in pounds) and volumes
of containers are recorded on DD Forms 1348-1A for all hazardous waste and
universal waste containers being turned in to the 90-HWAS. If scales are not
available at the HWSAP, the weight may be added to the form at the 90-HWAS.
i. Ensure appropriate and authorized containers are used that are capable of being
labeled, handled, loaded, and transported following management procedures in
the areas where hazardous and universal wastes are being generated in their
activities.
j. Ensure hazardous waste at the HWSAP is removed within three calendar days of
reaching the accumulation volume limit of 55 gallons of hazardous waste or one
quart of acutely hazardous waste and are turned in to the 90-HWAS.
SECTION THREE Responsibilities
3-6
k. Ensure that universal waste containers are moved to a 90-HWAS within six months
of the start date.
l. Maintain hazardous waste containers in proper condition, e.g., no pitting, no sharp
edge creases or dents, no material defects, no bulging heads, and no excessive
rust.
m. Ensure that containers are kept closed except when they are being filled.
n. Ensure proper segregation into containers to prevent co-mingling with other
hazardous or non-hazardous materials.
o. Maintain Site Specific Spill Plans for each of their activities using USAACE Form
2719, which is found in Appendix T.
p. Ensure that personnel (including themselves) who handle hazardous waste in their
areas of responsibility are trained as appropriate to the duties that they perform.
HWSAP managers should annually attend the HWSAP Manager Course offered
by DPW-ENRD. HWSAP managers may also attend the DOD HM/HW Handler
Course if recommended by their supervisors, but this training is not required for
HWSAP managers.
q. Ensure that an approved fire extinguisher is readily available if flammable
hazardous waste is handled at the HWSAP.
r. Ensure that a spill kit is accessible in areas where liquid wastes are generated.
s. Perform weekly inspections of the HWSAP. Personnel should use USAACE Form
2725, HWSAP Inspection Checklist, for weekly (every 7 days) inspections. A copy
of this checklist may be found in Appendix E, but the official version of all EMS
documents is maintained on the Sustainable Fort Rucker website.
3.6 90-HWAS MANAGERS
The 90-HWAS Managers are the supervisors directly responsible for the hazardous waste
being stored at the 90-HWAS.
a. Ensure that they have an up-to-date appointment letter from their supervisor or
commander using USAACE Form 2733, HWSAP and HWAS Manager
Appointment Memo (see Appendix D), and that the letter has been submitted to
the DPW-ENRD prior to performing the required tasks. At a minimum, each site
SECTION THREE Responsibilities
3-7
will have an accumulation site manager and an alternate manager formally
appointed, and each manager will have received initial and annual refresher
training in accordance with applicable federal and state regulations.
b. Attend training specified by DPW-ENRD, including the initial DOD HM/HW Handler
Course and annual refresher course as well as the DPW-ENRD 90-HWAS
Manager Course annually.
c. Coordinate with DPW-ENRD if relocation of a 90-HWAS is necessary.
d. Act as initial spill coordinators until the installation on-scene coordinator arrives in
the event of a hazardous waste spill in their areas of responsibility. Any person
discovering a spill or release of a hazardous substance or waste must immediately
report the incident to his/her supervisor.
e. Ensure accountability of all hazardous waste by maintaining an inventory of wastes
at each site. Inventories will include the accumulation start date, the date the
container was received within the site, the date the container was removed from
the site, the document number on the DD Form 1348-1A and the profile number of
each container.
f. Ensure that appropriate EPA Markings are on the hazardous waste label or
container to include the EPA ID number, the words "HAZARDOUS WASTE",
proper shipping name, EPA Waste Code(s), and Accumulation Start Date.
g. Ensure that hazardous waste is managed in accordance with the Fort Rucker
HWMP and appropriate federal, state, local, and Army regulations.
h. Ensure that containers are properly segregated and compatible with the waste.
Advise the Hazardous Waste Program Manager of any changes in chemicals or
processes that may impact the appropriate EPA markings on the waste container.
i. Inspect and document assigned 90-HWAS weekly (every 7 days) using USAACE
Form 2726, HW 90-Day Accumulation Area Inspection Log. A copy of this form is
located in Appendix E.
j. Ensure the appropriate warning signs are posted at all approaches to the 90-
HWAS. Signs are to include the words “Hazardous Waste Accumulation Site”, and
“In Case of Emergency Call (telephone number)”.
SECTION THREE Responsibilities
3-8
k. Ensure the DD Form 1348-1A is completed when receiving a waste container. For
Cairns, Shell, and Main Post 90-HWAS, submit copies of the completed DD 1348-
1A to DPW-ENRD weekly.
l. Ensure that a communication device, a spill kit, and the Site Specific Spill Plan are
available at (or near) the 90-HWAS.
m. Ensure that an approved fire extinguisher is readily available if flammable
hazardous waste is handled at the 90-HWAS.
n. Maintain on file all hazardous waste management records and documents for the
specific accumulation site, in accordance with procedures outlined in Section 5 of
this HWMP. For Cairns, Shell, and Main Post 90-HWAS, report containers in a 90-
HWAS over 60 days to DPW-ENRD. For Hanchey, Lowe, and AMSS, transfer
waste to the Main Post 90-HWAS within two weeks of receipt.
3.7 PERSONNEL WORKING WITH HAZARDOUS WASTES
a. Contain and clean-up spills of known materials immediately when practical, and
follow the procedures in the Site Specific Spill Plan for the work site.
b. Report hazardous waste spills to supervisor or commander. See the ISCP and
Spill Prevention, Control, and Countermeasures (SPCC) Plan for additional
information.
c. Place hazardous waste in designated containers that are properly labeled for the
waste.
d. Never place hazardous waste in a trash container or dumpster. Also, never pour
waste down a sanitary or storm drain or on the ground. Properly manage all
hazardous waste in accordance with this HWMP.
e. Wear the appropriate protective clothing when handling hazardous wastes.
f. Seek the appropriate training from their supervisors to perform specific jobs.
3.8 EO AND EPOC
a. Attend the two-day Environmental Officer Training Course upon initial assignment
and the 4-hour refresher course annually. Only the 4-hour course is required for
EPOCs.
b. Serve as the organization’s primary environmental contact.
SECTION THREE Responsibilities
3-9
c. Ensure implementation and compliance with this plan for their organization.
d. Manage the organization’s environmental training and certification records.
e. Identify all organizational positions that require mandated training, such as
hazardous waste management.
f. Conduct on-the-job training for shop-level personnel.
3.9 DIRECTOR OF PUBLIC WORKS
a. Oversees the administration of the hazardous waste management program.
b. Provides resources for the overall management of the Fort Rucker EMS.
c. Ensures proper submittal of all permits, manifests, audits, checklists, reports,
plans, and payments of fees or fines, as required by DOD, Army, federal, and state
regulatory agencies.
d. Ensures DPW-ENRD has all resources necessary to implement the hazardous
waste requirements described in this plan.
e. Coordinates all inspections of Fort Rucker by federal and state regulatory
agencies.
3.10 DPW-ENRD
a. Manages the installation hazardous waste management program and develops
overall management policies for HW, including but not limited to hazardous waste
accumulation and storage policies, on-site auditing/inspection procedures, and
turn-in procedures.
b. Incorporates hazardous waste objectives and targets into the EMS utilizing
USAACE Form 2724, Objectives and Targets Action Plan.
c. Develops, implements, updates, maintains, and distributes an overall Hazardous
Waste Management Plan for the installation, which includes guidance to all
activities for the proper handling of hazardous waste.
d. Signs hazardous waste manifests, as delegated by the Garrison Commander, and
prepares hazardous waste reports and compliance documentation as required by
federal, state, local, and Army regulations. Ensures appropriate hazardous waste
manifests are prepared for hazardous waste in accordance with DOT, ADEM, and
EPA requirements for transportation and disposal, respectively. Manages manifest
SECTION THREE Responsibilities
3-10
requirements, including signing for the commander, tracking manifest from cradle-
to-grave, publishing exception reports, and maintaining other associated
documentation, as required, for all waste not shipped through the Defense
Logistics Agency Disposition Services (DLADS).
e. Perform and maintain records of hazardous waste quarterly compliance
inspections conducted using USAACE Form 2717, Environmental Compliance
Inspection Checklist. A copy of the sections applicable to hazardous waste
management is included in Appendix E.
f. Prepares permit applications as required.
g. Assists organizations by providing guidance with hazardous waste
characterization, accumulation, storage, marking and labeling, waste minimization,
waste recycling, and waste turn-in and disposal.
h. Profiles waste streams generated by the installation activities based on information
provided by the installation, tenant, and contract organization managers; SDSs; or
laboratory analysis.
i. Coordinates and submits required regulatory reports and documents relating to the
installation's hazardous waste management program except as otherwise directed
by the Garrison Commander.
j. Maintains files of reports, documents, and records required by pertinent
environmental laws and regulations.
k. Coordinates the establishment and/or relocation of HWSAPs and 90-HWASs in
support of the performance of organization’s missions. Ensures that the
establishing of these storage areas is in accordance with the requirements of
Sections 5 and 6.
l. Serves as the technical director and advisor for mandatory hazardous waste
training programs that provide required training for all organization EOs and
hazardous waste handlers.
m. Maintains an inventory of hazardous waste on the installation through the use of
hazardous waste turn-in documentation submitted by generating activities.
SECTION THREE Responsibilities
3-11
n. Conducts periodic inspections of generator accumulation points and areas to
ensure that hazardous waste is being handled, stored, and turned in according to
the policies and procedures set forth in this HWMP.
o. Provides ongoing guidance to generating activities for the proper handling and
disposal of hazardous waste.
p. Monitors the progress of all activities in achieving the hazardous waste reduction
goals approved in the installation Pollution Prevention Plan.
3.11 DEFENSE LOGISTICS AGENCY DISPOSITION SERVICES (DLADS) EGLIN
The Defense Reutilization and Marketing Office (DRMO) has changed its name to the
Defense Logistics Agency Disposition Service (DLADS). The services offered by DLADS
are essentially the same as those previously provided by DRMO. DPW-ENRD will assist
organizations with any process modifications that may result from this change.
a. Coordinate timely disposition of hazardous waste to off-site permitted TSD facilities
by providing contracting support for procurement of hazardous waste
transportation and disposal services as well as hazardous property reutilizations.
b. Travel to Fort Rucker each time there is a hazardous waste pick-up by the
hazardous waste disposal contractor and serve as the Contracting Officer’s
Representative.
c. Ensure that the transporter is properly certified by the EPA, the State of Alabama,
and other states to transport hazardous waste and that the transporter provides
both a vehicle and a driver licensed to load and haul hazardous waste.
d. Ensure that the contracted disposal services comply with federal and state
hazardous waste regulations.
e. Verify accuracy of hazardous waste weight measurements prior to waste
acceptance.
3.12 PUBLIC AFFAIRS OFFICE (PAO)
a. Acts as the focal point for inquiries from the news media and concerned citizens
regarding hazardous waste and in the event of a hazardous waste incident or
accident.
SECTION THREE Responsibilities
3-12
b. Assists the on-scene coordinator during hazardous waste incidents by keeping
interested news media and the public aware of events and curtailing rumors
through the dissemination of coordinated, accurate information. Responds to the
accident/incident site, to the command post, and to the Public Affairs duty section
where an information center may be established.
c. The presence of hazardous waste in a contained area will probably not constitute
reasonable cause to forcibly deny access to the area by accredited news media
representatives. Applicable security and safety provisions will apply, however.
Under no circumstances will Public Affairs Office (PAO) personnel escort news
media representatives into a hazardous or potentially dangerous area without
permission from the on-scene coordinator.
3.13 LOGISTICS READINESS CENTER (LRC)
a. Manages hazardous material requisition, receipt, and distribution through the
Hazardous Material Control Center (HMCC).
b. Inducts all organizations and activities on Fort Rucker into the HMCC system and
implements product substitution, shelf-life management, and proper storage
requirements.
c. Maintains online SDS database.
3.14 CIVILIAN PERSONNEL ADVISORY CENTER (CPAC)
a. Validates training and ensures job descriptions are amended for all civilian
employees involved with hazardous waste management/training.
SECTION FOUR Hazardous Waste Identification and Classification
4-1
Section 4 Hazardous Waste Identification and Classification
4.1 GENERAL
Solid waste is any garbage, refuse, sludge, liquid, semi-solid, or contained gaseous
material resulting from industrial, commercial, mining, and agricultural activity. A material
is a solid waste after it has been used for its intended purpose, when it is discarded by
being abandoned, and sometimes when it is recycled. After an item has been determined
to be a solid waste, a hazardous waste determination must be made. Please contact the
DPW-ENRD Hazardous Waste Program Manager for assistance. All hazardous wastes
must meet the following criteria:
• Not specifically excluded or exempted by RCRA; and
• Is a RCRA “Listed” waste, or
• Exhibits a characteristic of hazardous waste.
4.2 EXEMPTIONS FROM HAZARDOUS WASTE DEFINITION
ADEM Administrative Code 335-14-2-.01(4)(a)-(b) and 40 CFR 261.4 define materials
that are exempt from definition as a hazardous waste. Exemptions from RCRA hazardous
waste commonly encountered at Fort Rucker include:
• Household waste (ADEM Administrative Code 335-14-2-.01(4)(b)1 / 40 CFR
261.4(b)(1)).
• Solid waste consisting of discarded arsenical-treated wood (pressure treated
lumber) or wood products which fails the test for the Toxicity Characteristic (waste
codes D004 to D017) and is not a hazardous waste for any other reason if the
waste is generated by persons who use the arsenical-treated wood and wood
products (ADEM Administrative Code 335-14-2-.01(4)(b)9 / 40 CFR 261.4(b)(9)).
• Petroleum-contaminated media and debris that fail the test for the Toxicity
Characteristic of ADEM Administrative Code 335-14-2-.03(5) / 40 CFR 261.24
(Waste Code D018 through D043) and are subject to the corrective action
regulation under 40 CFR 280 (ADEM Administrative Code 335-14-2-.01(4)(b)10 /
40 CFR 261.4(b)(10)).
• Used chlorofluorocarbon refrigerants from totally enclosed heat transfer
equipment, including mobile air conditioning systems, mobile refrigeration, and
SECTION FOUR Hazardous Waste Identification and Classification
4-2
commercial and industrial air conditioning and refrigeration systems that use
chlorofluorocarbons as the heat transfer fluid in a refrigeration cycle, provided the
refrigerant is reclaimed for further use (ADEM Administrative Code 335-14-2-
.01(4)(b)12 / 40 CFR 261.4(b)(12)).
• Used oil filters that are not terne plated, provided that they are drained of oil using
one of the regulatory-specified methods (ADEM Administrative Code 335-14-2-
.01(4)(b)13 / 40 CFR 261.4(b)(13)).
• Domestic sewage and any mixture of domestic sewage and other wastes that
passes through a sewer system to a publicly-owned treatment works for treatment
(ADEM Administrative Code 335-14-2-.01(4)(a)1 / 40 CFR 261.4(a)(1).
• Scrap metal being recycled (ADEM Administrative Code 335-14-2-.01(4)(a)13 / 40
CFR 261.4(a)(13)).
4.3 LISTED WASTES
Hazardous waste identification and classification is conducted according to the guidance
of ADEM Administrative Code 335-14-2 / 40 CFR 261. Listed wastes are wastes that have
been deemed harmful to human health and the environment. State and federal
regulations define four categories of listed wastes:
• F - List: Non-specific sources (ADEM Administrative Code 335-14-2-.04(2) / 40
CFR 261.31).
• K - List: Specific sources (ADEM Administrative Code 335-14-2-.04(3) / 40 CFR
261.32).
• P - List: Pure or commercial grade formulations of certain specific unused
chemicals that are acutely hazardous (ADEM Administrative Code 335-14-2-.04(4)
/ 40 CFR 261.33). This list also includes the listed items when they are residues
remaining in the containers, contaminated solid, water or other debris resulting
from the cleanup of a spill with the P-listed waste as the major ingredient.
• U - List: Pure or commercial grade formulations of certain specific unused
chemicals (ADEM Administrative Code 335-14-2-.04(5) / 40 CFR 261.33). This list
also includes the listed items when they are residues remaining in the containers,
SECTION FOUR Hazardous Waste Identification and Classification
4-3
contaminated solid, water or other debris resulting from the cleanup of a spill with
the U-listed waste as the major ingredient.
4.4 CHARACTERISTIC WASTES
A characteristic waste is a waste that is not excluded that exhibits one of the four
characteristics defined in 40 CFR Part 261 Subpart C - ignitability (D001), corrosivity
(D002), reactivity (D003), and toxicity (D004 - D043). The characteristic waste codes may
be applicable to wastes that are listed as described in Section 4.3 above as well as to
wastes that are not listed.
The characteristic of ignitability (Waste Code D001) is defined in ADEM Administrative
Code 335-14-2-.03(2) / 40 CFR 261.21. According to this regulation, a liquid waste is
considered ignitable when it has a flash point less than 140 degrees Fahrenheit. Some
examples commonly found in motor pools, material storage locations, and HWSAPs are
paints, paint thinners, wax removers, waste ink, M256A1 (chemical agent detection) kits,
and dry cleaning solvents. A non-liquid waste is considered ignitable when, under
standard temperature and pressure, it is capable of spontaneous and sustained
combustion, such as solvent rags or paint rags. A waste also exhibits the characteristic
of ignitability if it is an ignitable compressed gas as defined by ADEM Administrative Code
335-14-2-.03(2)(a)3 / 49 CFR 173.300 or if it is an oxidizer as defined by ADEM
Administrative Code 335-14-2-.03(2)(a)4 / 49 CFR 173.151.
The characteristic of corrosivity (Waste Code D002) is defined in ADEM Administrative
Code 335-14-2-.03(3) / 40 CFR 261.22. A waste is corrosive when it is an aqueous
solution with a pH of less than or equal to 2 or greater than or equal to 12.5. A liquid waste
is a corrosive waste when it corrodes steel at a rate greater than 1/4 inch per year at a
test temperature of 130 degrees Fahrenheit. Some examples of corrosive wastes are
nitric acid, phosphoric acid, battery acids, rust removers, etching fluids, alkaline
degreasers, lime and water mixtures, decontamination solution number 2 (DS2), and
sodium hydroxide.
The characteristic of reactivity (Waste Code D003) is defined in ADEM Administrative
Code 335-14-2-.03(4) / 40 CFR 261.23. Examples of reactive wastes are calcium
hypochlorite, flameless ration heaters (FRH) from meals-ready-to-eat (MRE), and
SECTION FOUR Hazardous Waste Identification and Classification
4-4
unexpended military munitions. A waste is considered reactive when it meets any of the
following conditions:
• Normally unstable and readily undergoes violent change without detonating.
• Reacts violently with water.
• Forms potentially explosive mixtures with water.
• Generates toxic gases, vapors, or fumes when mixed with water.
• Is capable of detonation or explosive reaction if it is subjected to a strong initiating
source or if heated under confinement.
• Is readily capable of detonation or explosive decomposition or reaction at standard
temperature and pressure.
• Forbidden explosive as defined in 49 CFR 173.51, or a Class/Division 1.1, 1.2, or
1.3 explosive as defined in 49 CFR 173.50. Examples are nitroglycerin, super
tropical bleach (STB), and sodium metal.
The characteristic of toxicity (Waste Codes D004-D043) is defined in ADEM
Administrative Code 335-14-2-.03(5) / 40 CFR 261.24. A solid waste exhibits the
characteristics of toxicity if an extract from a representative sample of the waste contains
any of the contaminants listed in the following table at a concentration equal to or greater
than the respective value given in the table. Some examples commonly found are
insecticides, mercury batteries, cadmium, lindane, terne plated (alloy of tin and lead) oil
filters, used photo solution containing silver, lead-acid batteries, and lead-based paint
(LBP) chips.
4.5 FORT RUCKER WASTE IDENTIFICATION REQUIREMENTS
Under RCRA regulations, it is the responsibility of the organization that generates or owns
a hazardous waste to properly and accurately identify the contents of all containers
holding hazardous waste. The Hazardous Waste Program Manager is responsible for
profiling each waste stream generated at Fort Rucker. Hazardous waste will be identified
by common name, EPA hazard characteristic, and waste codes during its accumulation
at the point of generation (e.g. the HWSAP). This is generally based upon product SDS
and user knowledge of the process producing the waste, since most generators have
well-established procedures and processes that produce known waste streams. The
SECTION FOUR Hazardous Waste Identification and Classification
4-5
waste profile may also use laboratory analysis of the waste stream. Each generator is
required to provide information on changes in waste streams as a result of a process or
chemical change to DPW-ENRD prior to implementation.
SECTION FOUR Hazardous Waste Identification and Classification
4-6
Table 4-1 Maximum Concentration of Contaminants for the Toxicity Characteristic
EPA WASTE CODE CONTAMINANT REGULATORY LEVEL
(mg/L) D004 Arsenic 5.0 D005 Barium 100.0 D018 Benzene 0.5 D006 Cadmium 1.0 D019 Carbon tetrachloride 0.5 D020 Chlordane 0.03 D021 Chlorobenzene 100.0 D022 Chloroform 6.0 D007 Chromium 5.0 D023 o-Cresol* 200.0 D024 m-Cresol* 200.0 D025 p-Cresol* 200.0 D026 Total Cresol* 200.0 D016 2,4-D 10.0 D027 1,4-Dichlorobenzene 7.5 D028 1,2-Dichloroethane 0.5 D029 1,1-Dichloroethylene 0.7 D030 2,4-Dichlorotoluene 0.13 D012 Endrin 0.02 D031 Heptachlor (and its epoxide) 0.008 D032 Hexachlorobenzene 0.13 D033 Hexachlorobutadiene 0.5 D034 Hexachloromethane 3.0 D008 Lead 5.0 D013 Lindane 0.4 D009 Mercury 0.2 D014 Methoxychlor 10.0 D035 Methyl ethyl ketone 200.0 D036 Nitrobenzene 2.0 D037 Pentachlorophenol 100.0 D038 Pyridine 5.0 D010 Selenium 1.0 D011 Silver 5.0 D039 Tetrachloroethylene 0.7 D015 Toxaphene 0.5 D040 Trichloroethylene 0.5 D041 2,4,5-Trichlorophenol 400.0 D042 2,4,6-Trichlorophenol 2.0 D017 2,4,5-TP (Silver) 1.0 D043 Vinyl chloride 0.2
SECTION FIVE Hazardous Waste Satellite Accumulation Points
5-1
Section 5 Hazardous Waste Satellite Accumulation Points
5.1 GENERAL
A HWSAP is a point of generation at which a maximum of 55-gallons of hazardous waste
or one quart of acutely hazardous waste is accumulated over an indefinite period of time
and is controlled by the operator generating the waste. The 55-gallon limit applies to the
total of all the non-acutely hazardous waste accumulated at a HWSAP. In accordance
with the ADEM interpretation letter dated 26 April 2005, each waste stream from a
generating process may be considered a separate HWSAP even if they are located in the
same area if they are managed in accordance with regulatory guidelines (see Section 5.3
below for additional details). A copy of this letter is included in Appendix F.
Generators in a shop, laboratory, or other work area where small amounts of waste are
produced generally use this type of accumulation area. Each HWSAP must be located at
or near the area where the waste is generated and must be under the direct control of the
organization generating the waste.
Fort Rucker has approximately 75 HWSAPs located throughout the installation. Based on
organization missions, HWSAPs may change due to deployments or other factors. DPW-
ENRD tracks the establishment and closure of HWSAPs. The Hazardous Waste Program
Manager maintains a list of the HWSAPs.
5.2 HWSAP MANAGERS
A HWSAP manager and an alternate manager shall be formally assigned/appointed to
maintain the area in accordance with the requirements of this section using USAACE
Form 2733, HWSAP and HWAS Manager Appointment Memo, a copy of which is located
in Appendix D. These HWSAP Managers must receive documented training for
familiarization of this plan, the chemicals they will be working with and applicable RCRA
regulations.
See Section 3.5 for responsibilities of the HWSAP managers.
SECTION FIVE Hazardous Waste Satellite Accumulation Points
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5.3 WASTE ACCUMULATION QUANTITIES
A generator may accumulate up to 55-gallons of hazardous waste or one quart of acutely
hazardous waste in a HWSAP at or near any point of generation where wastes initially
accumulate and must be under the control of the operator generating the waste.
Neither the regulations nor the preamble to the regulations expressly defines the terms
“at or near the point of generation” or “under the control of the operator” with reference to
the distance from the point of generation or the level of control required. Therefore, DPW-
ENRD can evaluate each situation on a case-by-case basis in order to determine if a
storage area qualifies as a satellite accumulation area.
ADEM has determined that it is permissible to have adjacent HWSAPs provided that
a. Each HWSAP is for a separate waste stream.
b. The HWSAP sign clearly identifies each separate waste stream (i.e., one waste
stream for solid paint filters and one waste stream for liquid paint wastes).
c. Each waste stream does not exceed the 55-gallon or 1-quart limit.
d. Each container is labeled with the words "Hazardous Waste" or with other words
that identify the contents of the containers in accordance with ADEM
Administrative Code 335-14-3-.03(5)(c)(ii) / 40 CFR 262.34(c).
e. Incompatible wastes are stored separately.
When a generator accumulates more than 55-gallons of hazardous waste or one-quart of
acutely hazardous waste, personnel should mark the container with the date on which the
threshold is exceeded and remove the container within three consecutive days to the 90-
HWAS.
Fort Rucker uses interim containers for collecting hazardous waste in many work areas.
These containers will meet all requirements for managing a HWSAP with the exception
of weekly inspections. ADEM does not limit the use of white step cans to a certain area
or shop, or access to a certain HWSAP, but rather to the obeying of HWSAP rules at each
location. Section 5.4 contains information about container management requirements,
including these interim containers. Additional details are available in the ADEM
SECTION FIVE Hazardous Waste Satellite Accumulation Points
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correspondence dated April 25, 2005 regarding clarifications of installation HWSAP
requirements. A copy of the ADEM correspondence is included in Appendix F.
5.4 CONTAINER MANAGEMENT REQUIREMENTS
5.4.1 Compatibility Only containers approved by DPW-ENRD may be used to accumulate hazardous wastes.
Wastes are only stored in containers compatible with waste materials. Incompatible
wastes must not be consolidated and collected in the same container. Only compatible
wastes will be stored together. In summary, these compatibility guidelines are followed:
• Segregate reactive wastes from ignitable wastes.
• Segregate acids from caustics.
• Segregate corrosives from flammables.
• Segregate oxidizers from all other wastes.
5.4.2 General Requirements The following general requirements should be implemented in all HWSAPs:
1. All containers must be maintained in good condition with no dents, corrosion,
leaks, noticeable spills, or bulging. If a container leaks, waste should be transferred
to another container or overpacked.
2. Containers must be stored in a manner such as to avoid direct contact with the
foundation or flooring by the use of pallets or other suitable device to facilitate
inspections.
3. Containers of highly flammable wastes must be properly grounded.
4. If the accumulation area is enclosed, adequate ventilation and lighting must be
provided.
5. If the accumulation area is not enclosed, it must be protected from direct sunlight
and inclement weather.
6. Waste containers must be closed at all times, except when it is necessary to add
or remove waste from the container. If a container with a funnel or funnel device
(securely attached and consistently used) is to be considered a “closed container,”
the funnel must have a lid equipped with a seal (ball valve) and latching/locking
mechanism to secure it when waste is not being poured or added to the container.
SECTION FIVE Hazardous Waste Satellite Accumulation Points
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7. Sufficient aisle space must be maintained in accumulation areas to allow for the
unobstructed movement of personnel, fire protection equipment, spill control
equipment, and decontamination equipment.
5.4.3 Liquid Waste Container Requirements A means of secondary containment (for the entire volume of the container) must be used
for liquids such as placement of containers in appropriately sized containment pallets,
drip pans, or impermeable berms. Liquid wastes should be containerized in closed top
drums equipped with a bung rather than an open top drum to minimize the potential for
accidental spills and releases.
5.4.4 Labels and Signs Hazardous waste containers must be marked clearly with the words "HAZARDOUS
WASTE", a description of the contents, the hazardous waste code(s), and the EPA ID
number.
Each HWSAP will be posted with a sign with the words "Hazardous Waste Satellite
Accumulation Point". It is required that the HWSAP Manager’s and Alternate HWSAP
Manager’s name and contact telephone number/extension information also be included
on this sign.
5.4.5 Interim Container Management A single HWSAP may have multiple points of generation. Generators may transfer
hazardous waste between rooms within a single building and/or containers to facilitate
proper management. Fort Rucker has implemented a process in which interim HWSAPs
are used in work areas for accumulating waste during operations. These interim HWSAPs
are primarily used for accumulated rags and other absorbent materials at individual work
stations. These containers must meet all regulatory requirements for a HWSAP, but they
are required to be emptied at the end of each shift into a consolidated HWSAP with
additional management requirements (i.e., weekly inspections).
5.5 SECURITY
HWSAPs usually consist of one container stored within operational areas in compliance
with the requirement to be at or near the point of generation. These operational areas are
SECTION FIVE Hazardous Waste Satellite Accumulation Points
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located within secure facilities, such as motorpools, hangars, or buildings, which have
provisions for security to prevent entry by unauthorized personnel. All entrances will be
locked when facilities are not occupied. Signs and labels will include the words
“HAZARDOUS WASTE” as specified in Section 5.4.4. Also, Fort Rucker is considered a
secure installation, which prevents unauthorized access to these facilities.
5.6 SPILL PREVENTION AND RESPONSE
Each HWSAP storing a liquid waste is required to have an impervious spill containment
system with sufficient capacity for containers (ability to contain 10 percent of the total
volume of all containers or the volume of the largest container, whichever is greater).
Lined or unlined sandbag dikes and asphalt pavements are not acceptable unless a berm
is constructed in a manner which would prevent migration of a spill or leak.
HWSAPs will not be located near storm drains, sewer drains, or washracks. Washracks
with oil/water separators do not serve as secondary containment and should not be used
in this manner. Oil/water separators are designed to capture oil residue but not spills.
HWSAPs will be located in areas protected from the elements and in facilities that do not
allow rainwater to collect. If rainwater has collected, organizations will visually inspect the
water for signs of contamination. If the rainwater is contaminated, organizations will
contact DPW-ENRD for guidance about handling and disposing of this water. Otherwise,
organizations will discharge the water in accordance with established procedures. Fort
Rucker Form USAACE Form 2716, Secondary Containment Draining Activity Log
(Appendix G), will be maintained for each release of water from the HWSAP to show that
it was visually inspected for contamination prior to discharge.
Each HWSAP will develop a Site Specific Spill Plan utilizing USAACE Form 2719, Site
Specific Spill Plan. If requested, a copy of the Site Specific Spill Plan will also be submitted
to the Fire Department.
Basic fire, spill and safety equipment will be provided for each HWSAP. Equipment will
include, at a minimum, a fire extinguisher appropriate for the waste being accumulated
and spill cleanup material such as absorbent rolls or pads. This equipment shall be
located in the immediate area and be readily accessible to personnel in case of a spill or
SECTION FIVE Hazardous Waste Satellite Accumulation Points
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fire. All personnel involved with the HWSAPs shall be trained in the proper use of fire
equipment and spill material as well as the hazards associated with the waste.
HWSAP managers will ensure that all containers are closed, not leaking, and all spills or
releases are properly cleaned up and reported. Adequate spill control and containment
material must be on hand (within 50 feet of the HWSAP) to contain and clean up minor
spills. Upon discovery of a spill, personnel will attempt to stop the source of the spill, if
safe to do so, and notify the immediate supervisor or the Fort Rucker Fire Department at
911 if the supervisor is not available. All spills or releases must be cleaned up
immediately, with consideration for safety. The immediate area of the spill will be
evacuated to facilitate cleanup activities. Personnel will always use appropriate PPE.
The Fort Rucker Fire Department is the Installation On-Scene Commander at spill sites
until the emergency situation is secured and the situation is deemed safe for non-
emergency personnel to enter the spill control zone. DPW-ENRD then assumes control
of the spill site and coordinates spill cleanup. If contract help is required, DPW-ENRD
starts the contract mechanism process and requires reimbursement from the organization
involved. All organizations – including military, contractors, and civilians – and their
supervisors are financially and legally responsible for the cleanup of spills within their
areas.
5.7 INSPECTIONS
The HWSAP must be inspected weekly (every 7 days) using USAACE Form 2725,
HWSAP Inspection Checklist, located in Appendix E. If inspections reveal any
noncompliance, immediate action is taken to correct the deficiencies. Copies of all
inspections are kept for a minimum of three years. Inspections must be conducted by
someone who has attended the HWSAP Manager course provided by DPW-ENRD, which
is described in Section 5.8 below.
DPW-ENRD conducts environmental compliance inspections of all active hazardous
waste generation sites quarterly. These inspections are recorded on Fort Rucker Form
USAACE Form 2717, Environmental Compliance Inspection Checklist (Appendix E).
Additional assistance visits are performed on an as-needed or requested basis. DPW-
ENRD provides guidance to the organization for correcting deficiencies and conducts
SECTION FIVE Hazardous Waste Satellite Accumulation Points
5-7
follow-up inspections to ensure that deficiencies have been corrected. DPW-ENRD
reports the inspection results through the chain of command and assists installation
organizations with specific guidance required to obtain necessary training.
5.8 TRAINING
Training is required for personnel who handle hazardous waste and for managers and
supervisors of personnel, who handle hazardous waste, including those who maintain
and operate the HWSAPs in their shops and work areas (HWSAP Managers).
Initial personnel training shall begin within 60 days and be completed within six months
of the individual being assigned to hazardous waste handling duties. Training may consist
of formal classroom instruction, informal training (e.g., meetings, seminars, etc.), and/or
on-the-job training. Personnel trained in hazardous waste management procedures must
provide the training. At a minimum, the training program shall meet EPA and ADEM
regulatory requirements.
Training will focus on how to safely manage and operate a HWSAP. It must enable
employees involved with hazardous waste operations to perform their duties without
endangering themselves or other employees. Emphasis should be given to the
emergency response, use of protective equipment and clothing, recognition of hazardous
waste, hazards of waste encountered, and an overview of RCRA regulations as they
relate to employees.
DPW-ENRD offers a two hour HWSAP Manager Course that is required annually for all
personnel assigned as a primary or alternate HWSAP manager. This course meets all
regulatory requirements for training. Course offerings are listed on the Sustainable Fort
Rucker website (https://www.fortrucker-env.com).
All training will be documented and kept on file for three years from the date the employee
last worked at the organization/facility. Copies of annual Fort Rucker training certificates,
individual job descriptions, and training forms will be kept at each site that operates a
HWSAP. Organizations should use USAACE Form 2735, Hazardous Waste Job
Description and Training Record, to document training related to hazardous waste
specific for their job responsibilities. This form is not required if the organization has an
SECTION FIVE Hazardous Waste Satellite Accumulation Points
5-8
equivalent method for tracking their training, such as a database, that includes a job
description and information on the training received. The Hazardous Waste Program
Manager will make the determination as to whether the documentation is equivalent to
USAACE Form 2735. Approval of the usage of a different form must be in writing and
kept on file with the training records.
5.9 RECORDKEEPING
Individual activities and tenants will maintain the following records and documents and
maintain them in accordance with EMS-P008, Records Management Procedure, and
EMS-P002, Document Control Procedure:
5.9.1 Records that must be kept in the HWSAP a. Site Specific Spill Plan (USAACE Form 2719) first page with the location of the
entire plan noted
b. HWSAP inspection records (USAACE Form 2725)
5.9.2 Records that may be kept in a separate work area a. Complete Site Specific Spill Plan (USAACE Form 2719)
b. Fort Rucker HWMP (this document)
c. Hazardous waste training records, including USAACE Form 2735 (maintain for a
minimum of three years from when the employee last worked at the facility)
d. Fort Rucker ISCP and SPCC Plan
SECTION SIX Hazardous Waste Accumulation Sites
6-1
Section 6 Hazardous Waste Accumulation Sites
6.1 HAZARDOUS WASTE ACCUMULATION SITES
Each 90-HWAS is a temporary, non-permitted collection area where hazardous waste is
stored for less than 90-days (less than 180-days for a small quantity generator) pending
transfer to a permitted facility. This type of accumulation area may be used to store any
amount of hazardous waste from one or more HWSAPs, or it may serve a location where
an amount of hazardous waste over 55 gallons (or one quart acute hazardous waste) is
generated on a regular basis. The date of waste generation (accumulation start date) will
be the date that any amount of hazardous waste is first accumulated at the 90-HWAS
and shall be clearly marked and visible for inspection on each container.
Fort Rucker has five 90-HWAS, which are located at building 1207 (main 90-day HWAS),
Lowe, Hanchey, Cairns, and near building 1001 (the Aviation Maintenance Support Shop
[AMSS]). Shell has a 180-day HWAS, which is managed in the same manner as a 90-
HWAS.
The following criteria are followed when managing a 90-HWAS.
6.2 WASTE ACCUMULATION
Hazardous waste may accumulate at a 90-HWAS for no more than 90 days from the
accumulation start date. Once a container from a HWSAP has been transferred from a
HWSAP to a 90-HWAS, the site manager has up to 90 days from the accumulation start
date to arrange transfer to a permitted storage site. All waste should be turned in to the
main 90-day site within two weeks of transfer from the HWSAP, except waste generated
at Cairns and Shell. The main 90-HWAS is open every Thursday for turn in from 0900 to
1130 with no appointment required. Appointments may be scheduled for other times by
contacting the HMCC.
Organizations must turn in a completed DD Form 1348-1A, Issue Release/Receipt
Document, (Appendix H) with each waste turn in. Instructions on how to fill out the DD
1348-1A are included in EMS-WI-SW001 Waste Turn-In Procedure, which can be found
in Appendix K. Copies of the turn-in documentation will be kept for a minimum of three
years.
SECTION SIX Hazardous Waste Accumulation Sites
6-2
6.3 SIGNAGE
Signs identifying the area as a 90-HWAS, the hazards, and emergency contact
information must be conspicuously posted. Signs will be posted in container accumulation
sites that say: “HAZARDOUS WASTE ACCUMULATION POINT – AUTHORIZED
PERSONNEL ONLY” and “NO SMOKING WITHIN 50 FEET.” Signs must be visible from
all sides of the accumulation site and must be legible from a distance of at least 25 feet.
6.4 FACILITY SPECIFICATIONS
Each 90-HWAS is designed, constructed, maintained, and operated to minimize the
possibility of fire, explosion, or any unplanned sudden or non-sudden release of
hazardous waste or hazardous waste constituents to air, soil, or surface water that could
threaten human health or the environment. Container storage areas at each 90-HWAS
are protected from the elements, either in a covered area, inside the working area, or in
a separate building. If the 90-HWAS is located indoors, it will have adequate ventilation
provided. All 90-HWAS will have adequate lighting. All 90-HWAS are located in facilities
that minimize the potential for rainwater to collect. However, if rainwater is collected, the
Hazardous Waste Program Manager will evaluate the collected water in order to
determine the proper method of disposal.
Container storage areas shall have a containment system that is capable of collecting
and holding spills, leaks, and precipitation. Run-on of precipitation into the containment
system shall be prevented. Spilled or leaked waste and accumulated precipitation shall
be removed from the sump or collection area in as timely a manner as is necessary to
prevent overflow of the collection system. Acceptable containment systems include, as
applicable:
a. A sufficiently impervious underlying base for the containers, free of cracks or gaps,
to contain leaks, spills, and accumulated rainfall until the collected material is
detected and removed;
b. Efficient drainage design, so that standing liquid does not remain on the base
longer than one hour after a leakage or precipitation event, unless the containers
are elevated, or are in some other manner protected from contact with
accumulated liquids; and
SECTION SIX Hazardous Waste Accumulation Sites
6-3
c. Capacity sufficient to contain 10 percent of the total volume of all containers or the
volume of the largest container, whichever is greater.
Storage areas that store containers holding only non-liquid wastes need not have a
containment system provided that the storage area is sloped or otherwise designed and
operated to drain and remove liquid resulting from precipitation; or the containers are
elevated or are otherwise protected from contact with accumulated liquid.
Each 90-HWAS is provided with necessary communication equipment, including a
handheld two-way radio or accessible telephone. Fire control equipment appropriate for
the waste being accumulated must be located within 50 feet of the accumulation site.
Sufficient aisle space will be maintained in accumulation areas to allow for the
unobstructed movement of personnel, fire protection equipment, spill control equipment,
and decontamination equipment. Equipment will not be stored or parked in a manner that
would prohibit access to containers.
6.5 CONTAINER MANAGEMENT REQUIREMENTS
All wastes must be stored in accordance with ADEM Administrative Code 335-14-6-.09 /
40 CFR 265 Subpart I – Use and Management of Containers. The following specific
management procedures are followed at each of the 90-HWAS.
6.5.1 Container Stacking Containers that are 30-gallon or more will not be stacked more than two high. This
requirement applies to all containers, including cardboard boxes.
6.5.2 Container Specifications In general, only Department of Transportation/United Nations (DOT/UN) containers will
be used to accumulate hazardous wastes. All containers will be maintained in good
condition with no dents, corrosion, leaks, noticeable spills, or bulging. Containers must
be stored so as to avoid direct contact with the foundation or flooring by the use of pallets
or other suitable device to facilitate inspections.
Containers of ignitable or reactive waste will be located at least 50 feet from the
installation property line. Only non-sparking tools will be used when personnel are
working with containers that hold an ignitable waste. When transferring ignitable wastes
SECTION SIX Hazardous Waste Accumulation Sites
6-4
between containers, personnel will ensure that both containers are bonded to one another
and that both containers are properly grounded.
Containers must not be overfilled. In accordance with DOT requirements, liquid wastes
should only be stored in bung-type drums or cans. In order to allow for expansion of liquid
wastes resulting from temperature fluctuations and to prevent overflowing, the following
headspace guidelines are recommended:
• 55-gallon drum should have 3 to 4 inches of headspace
• 5-gallon cans should have 1.5 to 2 inches of headspace
• 1-gallon cans should have 1 inch of headspace
Containers must be closed at all times, except when it is necessary to add or remove
waste from the container. In general, waste should not be added to containers in the 90-
HWAS.
6.5.3 Waste and Container Compatibility Wastes must only be stored in containers compatible with waste materials. Hazardous
wastes shall be stored in containers that are chemically compatible with the waste. This
means that the containers used shall be made of or lined with materials that are non-
reactive with the hazardous waste to be stored, so that the integrity of the containers to
contain the waste is not compromised. For example, corrosive acids must not be placed
into a steel drum. Hazardous waste may not be placed in an unwashed container that
previously held an incompatible waste or material.
Incompatible wastes will not be consolidated and collected in the same container. Only
compatible materials will be stored together. Incompatible wastes should be physically
separated with different containment structures and as far apart as practical. A storage
container holding a hazardous waste that is incompatible with any waste or other
materials stored nearby in other containers shall be separated from the other materials or
protected from them by means of a dike, berm, wall, or other device. In summary, these
compatibility guidelines will be followed:
• Segregate reactive wastes from ignitable wastes
• Segregate acids from caustics
SECTION SIX Hazardous Waste Accumulation Sites
6-5
• Segregate corrosives from flammables
• Segregate oxidizers from all other wastes
6.5.4 Damaged Containers Hazardous wastes containers that are found to be leaking, corroded, or otherwise
deteriorated must be either transferred to a different container or over packed in DOT-
approved containers at any time during storage and prior to being turned in for disposal.
The over-pack container must be durable, non-leaking, compatible, and constructed to
safely contain the material being placed in it.
When using over-pack containers, ensure that an appropriate container is used in order
to prevent accident, personal injury, or costly cleanup of spills. Over-pack containers must
be marked and labeled the same way as any other container of hazardous waste.
6.5.5 Container Labeling In accordance with ADEM Administrative Code 335-14-3-.03(5)(a)2 and 3 / 40 CFR
262.34(a)(2) and (3), containers must be marked with the accumulation start date, the
EPA hazardous waste number, and with the words “HAZARDOUS WASTE.” Labels or
markings must be easily visible for inspection. In addition to the above requirements, the
following information should be included on the hazardous waste label that is affixed prior
to transportation for disposal, in accordance with ADEM Administrative Code 335-14-3-
.03(3)(b) / 49 CFR 172.304 requirements for marking containers:
• “HAZARDOUS WASTE - Federal Law Prohibits Improper Disposal. If found,
contact the nearest police or public safety authority or the U.S. Environmental
Protection Agency.”
• Generator's Name and Address
• Generator's EPA ID number
• Manifest Tracking Number
Each container will also be labeled in accordance with the requirements found in 49 CFR
172.400. Appendix I contains an excerpt of this regulation with the necessary table for
identifying required labels for each hazard class. The hazardous materials table in 49
SECTION SIX Hazardous Waste Accumulation Sites
6-6
CFR 172.101 lists the required labels for each hazardous substance that may be
transported.
A waste profile must be available for all hazardous wastes at the facility. The accumulation
start date will be marked on each container. If the waste comes from a HWSAP, the date
on the container is the date that the container was filled at the HWSAP prior to transfer to
the 90-HWAS. If waste is added to a new container at the 90-HWAS, the accumulation
start date is the date the first amount of waste was added to the container. If waste from
separate containers is combined, the accumulation state date will be the date for the
oldest waste that was combined.
Any drum with unknown contents must be marked “PENDING ANALYSIS” and the date
DPW-ENRD obtained a sample. When the analytical results are received, a waste profile
will be completed, and the container will be labeled appropriately. The accumulation start
date will be the date the sample was obtained. Records of any test results, waste
analyses, and waste determinations will be maintained for three years.
6.6 SECURITY
Each 90-HWAS is located within a secure area. All entrances will be locked when the
facilities are closed. Signs are posted with the wording “DANGER – UNAUTHORIZED
PERSONNEL KEEP OUT” at the entrance to each area. Signs are also posted with the
wording “HAZARDOUS WASTE AREA” and “NO SMOKING” where the hazardous waste
is actually stored. All signs should be legible from 25 feet away.
6.7 SPILL PREVENTION AND RESPONSE
The container accumulation areas at the 90-HWAS must have impervious containment
systems with sufficient capacity to contain 10 percent of the total volume of all containers
or the volume of the largest container, whichever is greater.
90-HWAS is required to have a Site Specific Spill Plan. As discussed in the ISCP,
USAACE Form 2719, Site Specific Spill Plan is required to be utilized. The first page of
USAACE Form 2719, Site Specific Spill Plan must be posted in a prominent place
adjacent to each 90-HWAS. The remainder of the plan must be placed in the location
SECTION SIX Hazardous Waste Accumulation Sites
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designated on page 1 of the form so that everyone involved in working at the site can
access and implement its contents.
Adequate spill control and containment materials will be stored within 50 feet of
accumulation sites to contain and clean up minor spills. All spills or releases will be
cleaned up immediately or as soon as it is safe to clean up the spill. All spill cleanup
materials will be disposed properly.
6.8 INSPECTIONS
Each 90-HWAS and its containers must be inspected weekly and each time waste is
placed in or removed from the site (see Appendix E for an inspection form, USAACE
Form 2726, HW 90-Day Accumulation Site Inspection Log). The site manager or other
individual performing the inspection will look for spills and leaks and for deterioration of
containers and the containment system. The inspector shall also check the accumulation
date on each container to ensure that no container holding hazardous waste is nearing
the 90-day limit. DPW-ENRD must be notified immediately if any container in the 90-day
site exceeds 60 days from the accumulation start date on the label. The inspection record
shall show the date of inspection, inspector's name, deficiencies noted, and corrective
actions implemented. The record containing this information will be maintained as
indicated in Section 6.10 Recordkeeping.
6.9 TRAINING
Training is required for personnel who handle hazardous waste and for managers and
supervisors of personnel who handle hazardous waste, including those who maintain and
operate the 90-HWAS.
Initial training will be completed within six months of designation. All employees must be
directly supervised until training is completed. Training consists of formal classroom
instruction, informal training (e.g., meetings, seminars, workshops, etc.), and on-the-job
training. Training records must be maintained on-site for a minimum of three years.
An annual review of the training is required not later than 365 days from the date of the
initial training session or prior annual training. Training records must be maintained on-
site for a minimum of three years.
SECTION SIX Hazardous Waste Accumulation Sites
6-8
Personnel trained in hazardous waste management procedures must provide the training.
At a minimum, the training program shall meet EPA and ADEM regulatory requirements.
Training will focus on how to safely manage and operate a RCRA hazardous waste
accumulation area. It must enable employees involved with hazardous waste operations
to perform their duties without endangering themselves or other employees. Emphasis
should be given to emergency response, use of protective equipment and clothing,
recognition of hazardous waste, hazards of the waste, and an overview of RCRA
regulations as they relate to employees.
The DOD Hazardous Materials and Hazardous Waste Handlers Course is taught each
year to meet these training requirements. The initial 24-hour course and the annual 8-
hour refresher course are required for all 90-HWAS Managers. DPW-ENRD also presents
a 90-HWAS Manager Course periodically that provides two hours of additional training to
address specific inspection, handling, and labeling requirements for the installation.
Organizations should use USAACE Form 2735, Hazardous Waste Job Description and
Training Record, to document training related to hazardous waste specific for their job
responsibilities. This form is not required if the organization has an equivalent method for
tracking their training, such as a database, that includes a job description and information
on the training received. The Hazardous Waste Program Manager will make the
determination as to whether the documentation is equivalent to USAACE Form 2735.
Approval of the usage of a different form must be in writing and kept on file with the
training records.
6.10 RECORDKEEPING
Individual activities and tenants will maintain the following records and documents and
maintain them in accordance with EMS-P008, Records Management Procedure, and
EMSP002, Document Control Procedure:
6.10.1 Records that must be kept in the 90-HWAS a. Site Specific Spill Plan (USAACE Form 2719)
b. 90-HWAS inspection records (USAACE Form 2726)
SECTION SIX Hazardous Waste Accumulation Sites
6-9
6.10.2 Records that may be kept in a separate work area a. Hazardous waste training records, including USAACE Form 2735 (maintain for a
minimum of three years from when the employee last worked at the facility)
b. Fort Rucker HWMP (this document)
c. Fort Rucker ISCP and SPCC Plan
d. DD Form 1348-1A turn-in documents
e. Manifests and Land Disposal Restrictions (Cairns, Shell, and Main 90-Day only)
f. Hazardous waste profile list
SECTION SIX Hazardous Waste Accumulation Sites
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SECTION SEVEN Hazardous Waste Disposal Procedures
7-1
Section 7 Hazardous Waste Disposal Procedures
7.1 GENERAL
DLADS is the primary method of disposal for hazardous waste generated by
organizations and activities on Fort Rucker. Alternate means of disposal may be used at
the discretion of the Hazardous Waste Program Manager. All hazardous waste disposed
through DLADS must be accomplished as quickly as possible to minimize liability for
environmental violations or spills.
Contractors that are not part of the normal operations of Fort Rucker, such as Corps of
Engineers construction contractors, should coordinate with DPW-ENRD prior to starting
work to ensure that procedures for hazardous waste disposal are established. In general,
these contractors will arrange for hazardous waste disposal separately from existing
installation hazardous waste contracts. Shipments of hazardous waste off-site must be
under the Fort Rucker EPA ID number, and all manifests will be signed by an authorized
representative in DPW-ENRD when the waste is not shipped through DLADS. EMS-WI-
SW010, Contractor Hazardous Waste Management, contains additional details about the
process that contractors should follow for properly managing their waste. A copy of this
work instruction is located in Appendix J.
7.2 HAZARDOUS MATERIAL REUSE EVALUATION
Much of the hazardous waste that is disposed each year is composed of unused
hazardous materials. In an effort to minimize the waste that is generated from unused
items, Fort Rucker has implemented a hazardous material reuse program. The process
is described below.
When an organization wishes to discard excess hazardous materials which are unopened
and/or are in good condition, the organization should bring the items to the HMCC (Bldg
1315) for evaluation. If possible, items will be added to the HMCC inventory, and
hazardous waste costs and liability will be avoided. Items with expired shelf life will be
researched by HMCC personnel and extended when possible.
7.3 PREPARATION FOR DISPOSAL AND PACKAGING
ADEM rule 335-14-3-.03 states that before transporting hazardous waste or offering
hazardous waste for transportation off-site, a generator must package the waste in
SECTION SEVEN Hazardous Waste Disposal Procedures
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accordance with the applicable U.S. DOT regulations on packaging under 49 CFR Parts
173, 178, and 179. For this reason, DPW-ENRD recommends storing waste at all
accumulation and storage sites on Fort Rucker in DOT-approved containers.
7.4 HAZARDOUS WASTE TURN IN PROCEDURES
Activities that generate hazardous waste and maintain HWSAPs will establish procedures
to ensure that all hazardous waste is turned in to a 90-HWAS within three days of the
date that the 55-gallon limit (or 1-quart of acutely hazardous waste limit) is reached. Both
the label and the turn-in document must accurately represent the contents of the
container.
The EMS Work Instruction (EMS-WI-SW001 Waste Turn-In Procedure) for hazardous
waste turn-in is provided in Appendix K. It specifies that activities must complete a DD
Form 1348-1A and have an active and approved Hazardous Waste Profile on file with
DPW-ENRD for each hazardous waste item to be turned in. Instructions on how to fill out
the DD 1348-1A are included in EMS-WI-SW001 with specific requirements of the Fort
Rucker 90-HWAS turn-in procedures.
Centralized 90-HWAS personnel will receive the waste, ensure that it is correctly labeled
and identified, and store it until it is picked-up by waste transport contractors. Waste that
is not properly labeled and identified or that is not properly packaged and safe to handle
will not be accepted at the accumulation area. Arrangements will have to be made by the
generating organization to immediately correct any situation that results in non-
acceptance of the hazardous waste at the 90-HWAS.
7.5 WASTE PROFILES
All wastes that are disposed through DLADS must have a waste profile completed to
characterize the waste. DPW-ENRD will prepare Hazardous Waste Profiles (Appendix L) using information gathered from SDS, analyses, or user process knowledge. Required
information includes generator name; USEPA ID and State ID; facility address; technical
contact’s name, title and telephone number; name of waste; waste code(s) (when
necessary); material characterization information (optional); RCRA characteristic
information; chemical composition information; material composition; shipping
SECTION SEVEN Hazardous Waste Disposal Procedures
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information; generator certification; toxicity characteristic information; hazardous waste or
non-RCRA identification; and DLADS verification information. Profiles will be created and
are stored electronically on the DPW-ENRD shared drive and in hardcopy.
When a new unprofiled waste is to be disposed, the SDS, any user knowledge, and any
additional information about the waste will be forwarded to DPW-ENRD. If waste
ingredients or chemical properties are unknown, items will be characterized prior to
disposal by DPW-ENRD. See Section 9 for information about Fort Rucker’s Hazardous
Waste Analysis Plan. At the time hazardous waste is placed in the 90-HWAS, the
organization will coordinate with DPW-ENRD to ensure waste containers are properly
labeled and meet any other packaging requirements. If an established waste stream
changes, DPW-ENRD will notify DLADS before shipping to ensure that the disposal
facility has the most updated information on the waste stream.
7.6 HAZARDOUS WASTE MARKING AND LABELING REQUIREMENTS
7.6.1 General Requirements State and Federal regulations have established specific labeling and marking
requirements for hazardous waste containers, which cross-reference the DOT regulations
contained in 49 CFR 172. All activities that generate hazardous waste at Fort Rucker will
comply with these requirements by accumulating hazardous wastes in appropriately
labeled and marked containers. The purpose of this is to facilitate the transport of waste
from generation/accumulation sites to the 90-HWAS and to facilitate subsequent
shipment for offsite disposal. The marking and labeling requirements of RCRA and DOT
regulations will, therefore, apply to all generators and shall be accomplished as described
in the following paragraphs.
• All labels shall be filled out using permanent ink that is not water-soluble and will
not readily fade. This helps to ensure that the information will not be inadvertently
smudged or otherwise rendered illegible resulting in personal injury or costly
analyses to re-identify the waste.
• A DOT Hazard Class Label such as "flammable", "corrosive," or "oxidizer," must
be applied to the container, when appropriate, if the container is being prepared
for shipment by a hazardous waste transporter. The DLADS contractor will apply
SECTION SEVEN Hazardous Waste Disposal Procedures
7-4
these DOT labels prior to shipment; however, these labels are not required for
containers in a HWSAP or 90-HWAS.
• Old labels and markings should be removed or painted over to ensure that there
is no confusion about the contents. New labels should not be placed over old ones.
7.6.2 Marking ADEM Rule 335-14-03(3) indicates that hazardous waste containers should be marked
in accordance with information in the DOT Hazardous Materials Transportation
regulations of 49 CFR 172. The labeling and marking standards require that hazardous
waste be marked in accordance with the DOT Hazardous Materials Table 49 CFR
172.101. This table sets out the proper shipping name, hazard class, ID number, packing
group, and other information that must be contained on DOT shipping papers for all
hazardous wastes. Steps outlined below give information necessary in order to comply
with DOT and additional ADEM 335-14-3 requirements. Regulations require that a
generator must mark each container of 110 gallons or less specifically in accordance with
the following requirements before waste is transported. The hazardous waste disposal
contractor combines like wastes and marks containers in accordance with DOT
regulations before waste is shipped off the installation per requirements below.
a. The marking must be durable, in English, and printed on or affixed to the surface
of a package or on a label, tag, or sign.
b. The marking must be displayed on a background of sharply contrasting color.
c. The marking must be unobscured by other labels or attachments and must be
located away from other marking that could substantially reduce its effectiveness.
d. In addition, RCRA regulations require that marking include the following statement:
i) HAZARDOUS WASTE - Federal Law Prohibits Improper Disposal. If found,
contact the nearest police or public safety authority or the U.S. EPA.
ii) Generators Name and Address ________________________
iii) Manifest Document Number ________________________
e. For 90-HWAS, hazardous waste labeling information must be placed on the
container as soon as the first hazardous waste is placed in it. HWSAPs do not put
a date on the waste until the containers reach 55-gallons for regular hazardous
waste and one quart for acutely hazardous waste. The HWSAP manager will
SECTION SEVEN Hazardous Waste Disposal Procedures
7-5
ensure that waste is turned in to the 90-HWAS within three consecutive days of
the date being placed on the hazardous waste label.
f. The site manager will ensure that the date upon which each period of accumulation
begins is clearly marked and visible for inspection on each container.
g. The information required by the preceding paragraphs is generally affixed to
containers storing hazardous waste by means of a label, which may have some of
the information required by item d above preprinted. This type of form label should
not be confused with, and is in addition to, the labeling requirements of Subsection
8.6.3 below. Appendix M provides several examples of container labels for
common Fort Rucker materials. Activities generating hazardous waste may obtain
these labels through the procurement system; however, in emergencies a limited
number of labels may be obtained by contacting DPW-ENRD.
7.6.3 Labeling Prior to shipment, each container must be labeled with a Hazard Class Label (i.e.,
flammable, corrosive, oxidizer) in accordance with the applicable RCRA (ADEM Rule
335-14-3-.03(2)) and cross-referenced DOT (49 CFR 172.400) regulations on hazardous
materials.
Hazard class labels are intended to provide identification of particular hazardous
properties of the material through pictorial representation. Labels are required by RCRA
on hazardous waste containers that will be shipped off-site. However, the DLADS
contractor will apply all necessary labels prior to shipment, and the DOT labels are not
required on wastes that are being accumulated in a HWSAP or 90-HWAS.
7.7 TURN-IN DOCUMENTATION
DPW-ENRD will ensure that turn in documentation (DD Form 1348-1A, Issue
Release/Receipt Document) required for disposal of hazardous waste through DLADS is
completed. Customers will generate the DD Form 1348-1A, Issue Release/Receipt
Document (Appendix H), for turn-in to HMCC or DPW-ENRD Hazardous Waste Program
Manager and for tracking purposes. See EMS-WI-SW001, Waste Turn-In Procedure for
details (Appendix K).
SECTION SEVEN Hazardous Waste Disposal Procedures
7-6
7.8 TRANSPORTATION OF HAZARDOUS WASTE
Off-post transportation of hazardous waste by any installation organization is strictly
forbidden. By state and federal regulations, Cairns and Shell Airfields are considered off-
post.
On-post transportation of hazardous wastes by generating activities shall be
accomplished in strict accordance with the following procedures: Vehicles used to
transport hazardous waste must meet the motor vehicle requirements of Army Regulation
385-10, Chapter 11-3, Motor Vehicle Safety Standards.
Hazardous wastes generated at Fort Rucker may be transported on post by the
generating organization from the generation point to a 90-HWAS. Generating activities
will establish control regarding personnel permitted to transport hazardous waste. These
controls should, at a minimum, require that all personnel involved with hazardous waste
transportation be trained in accordance with the requirements of Section 2.6 of this
document. Hazardous waste should not be transported from the generation point to a 90-
HWAS by forklift unless another transportation method is not feasible.
The following procedures should be followed for transferring containers from HWSAP to
90-HWAS:
a. Generating activities are responsible for arranging the loading and transportation
of hazardous waste using in-house support elements. If the organization does not
have the capability of transporting waste to a 90-HWAS from the HWSAP, DPW-
ENRD will provide pick-up assistance on a case-by-case basis.
b. Hazardous waste containers shall be secured during transportation in order to
avoid spills.
c. 55-gallon drums will be transported no more than one layer of three to a pallet to
ensure a stable load and avoid tipping over.
d. Cans of one gallon or more, stacked on pallets, will be stacked no more than two
deep in order to ensure a stable load and avoid tipping over. All other containers
will be transported in a way which ensures stable and safe transportation.
e. All containers shall be transported in an upright position.
SECTION SEVEN Hazardous Waste Disposal Procedures
7-7
f. Containers on pallets shall be banded, strapped, or positioned on the vehicle to
prevent tipping over. Caution must be exercised while banding, to avoid denting or
otherwise damaging containers.
g. Incompatible wastes shall not be transported on the same vehicle.
h. Unknown wastes are prohibited from transport except for a sample that is shipped
for testing and analyzing to determine its substance.
Hazardous wastes shall not be transported on any public road except by a State of
Alabama Licensed Hazardous Waste Transporter using a Hazardous Waste Manifest.
Personnel within DPW-ENRD are allowed to sign Hazardous Waste Manifests. They are
the only ones who have been granted signatory authority by the Garrison Commander.
All other off-post activities, which do not have prior authorization, must make
arrangements with an organization which is authorized to transport waste and sign the
manifest, or make other arrangements to provide for these requirements with appropriate
coordination and notification with DPW-ENRD.
Before any hazardous waste can be transported off-post, including waste generated by
contractors, it must be manifested in accordance with the requirements of Section 8.10,
with the contractor and Fort Rucker listed as the generator. Generators that manifest
waste on an irregular or infrequent basis should consult with DPW-ENRD about
appropriate profiling and manifesting procedures.
7.9 MANIFESTS
All generators who transport or contract for the transportation of hazardous waste for off-
site treatment, storage, or disposal must prepare a manifest. The manifest is a standard
EPA or state form, which lists the following:
• Generator's EPA ID number
• Generator's name and mailing address
• Generator's telephone number
• All transporter's names and EPA ID numbers
• Company name, site address, and EPA ID number for the facility designated to
receive the waste
SECTION SEVEN Hazardous Waste Disposal Procedures
7-8
• Number and type of containers holding the waste
• Total quantity of waste
• Weight or volume of the waste
• DOT description (including proper shipping name, hazard class, ID number, and
packing group)
• Special handling instructions and other information
• Emergency Response Guidebook reference number
• Generator's written certification that the statements made is true
The hazardous waste service contractor through the DLADS has the responsibility for
preparing the manifests for waste being transported from the Fort Rucker 90-HWAS. The
organization-level generators must supply supporting information and data for the
manifest preparation in the form of container labeling information and turn-in documents.
Once the DLADS contractor has completed the EPA or state manifest form, the
handwritten signature must be obtained from the initial transporter, DLADS personnel,
and DPW-ENRD personnel, along with the date of acceptance of the manifest. The
contractor must reproduce enough copies of the manifest to provide the generator (Fort
Rucker), HMCC, each transporter, the DLADS, Cairns Army Airfield, and Shell Army
Heliport. When shipment is made, the generator retains the generator copy of the
manifest and gives the initial transporter the remaining copies. Manifest copies will be
kept for a minimum of three years.
DPW-ENRD maintains information on EPA-approved RCRA TSD facilities and
transporters. All hazardous waste produced on Fort Rucker must be disposed through
DPW-ENRD. Only personnel in DPW-ENRD have been delegated authority by the
Garrison Commander to sign hazardous waste manifests.
7.10 EXCEPTION REPORTING
If the installation does not receive a copy of the hazardous waste manifest with the
signature of the owner, operator, or authorized representative of the designated TSD
Facility within 35 days of the date the waste was shipped from Fort Rucker, the status of
the waste must be determined. The transporter and the TSD facility must be contacted to
SECTION SEVEN Hazardous Waste Disposal Procedures
7-9
confirm that the waste shipment was in fact delivered and accepted, and to obtain a copy
of the manifest. If the waste was not delivered or accepted, the location of the waste must
be determined.
If the installation does not receive a copy of the closed manifest within 45 days of the date
the waste was accepted by the initial transporter, an exception report must be submitted
to ADEM. The exception report must include a legible copy of the manifest for which the
confirmation of delivery is missing and a cover letter describing efforts taken to locate the
hazardous waste and the results of those efforts.
DLADS is responsible for exception reporting for wastes shipped through their contractor.
7.11 RECORDKEEPING
Fort Rucker DPW-ENRD is responsible for preparing, submitting (where required) and
maintaining the following records:
a. The annual ADEM Form 8700-12 and the EPA Biennial Report for the entire
installation in accordance with ADEM Administrative Code 335-14-3-.04(2) and 40
CFR 262.41.
b. Records consisting of copies of manifests, exception reports, LDR notifications,
and incident reports. Maintain training records for DPW-ENRD personnel as well
as all 90-day accumulation site managers.
Individual activities and tenants will maintain the following records and documents and
maintain them in accordance with EMS-P008, Records Management Procedure, and
EMS-P002, Document Control Procedure:
a. Fort Rucker HWMP (this document)
b. 90-HWAS and HWSAP inspection records
c. Hazardous waste training records (maintain for a minimum of three years)
d. Fort Rucker ISCP and SPCC Plan
e. Site Specific Spill Plan
f. DD Form 1348-1A turn-in documents
Each 90-HWAS Manager is responsible for maintaining the following records:
a. Weekly inspection records for the 90-HWAS.
SECTION SEVEN Hazardous Waste Disposal Procedures
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b. Training records on personnel operating the 90-HWAS.
7.12 HAZARDOUS WASTE REPORTING
A biennial hazardous waste report will be submitted to the ADEM by DPW-ENRD based
on hazardous waste disposal records for each reporting year by 1 March. These reports
will be based on calendar year data. These reports will be forwarded by the ADEM to the
US EPA Region IV in accordance with federal hazardous waste regulations.
Fort Rucker is also required to annually complete and submit ADEM Form 8700-12,
Notification of Regulated Waste Activity by 15 October.
SECTION EIGHT Hazardous Waste Analysis Plan
8-1
Section 8 Hazardous Waste Analysis Plan
8.1 GENERAL
Wastes must be characterized prior to disposal. Chemical and physical characteristics of
a waste must be determined in order to develop a waste disposal profile and decide
disposal options. Information will be obtained by user or process knowledge, SDS or other
manufacturer information, or through laboratory analytical methods or other test methods.
If a laboratory analysis is required, the Hazardous Waste Program Manager will
coordinate sample collection and shipment to an appropriate analytical laboratory. After
receiving/reviewing the analytical results, the Hazardous Waste Program Manager will
advise the organization of disposal procedures and will complete a hazardous waste
profile sheet. The Hazardous Waste Program Manager will determine the extent of
testing. Waste characterizations will be forwarded to DLADS for recordkeeping and
forwarding to waste disposal facilities.
When analysis of a waste stream is required, additional time must be allowed for
processing the waste prior to disposal. At least 30 days will be allowed for the analysis
and profiling to occur prior to required removal from a 90-HWAS. Results for routine
laboratory analysis for hazardous waste determination purposes will usually be returned
to the installation within two weeks of submitting the waste sample. After receiving results,
the Hazardous Waste Program Manager must determine the waste codes associated
with the waste and complete waste profile documentation.
8.2 ANALYSIS COST
Waste analysis samples submitted through DPW-ENRD are part of the management
contract for the hazardous waste facility. An account is established with a certified lab for
any wastes that need to be analyzed. Organizations are typically not charged for the cost
of the analysis; however, a situation may arise (i.e., gross negligence) where the
organization may be required to pay for the lab analysis. The Chief, DPW-ENRD is
responsible for determining organization charges, as appropriate.
8.3 CHAIN-OF-CUSTODY FORMS
Chain-of-Custody forms are used for all samples collected. The environmental laboratory
receives all samples using these forms and assigns a unique sample number (from a
SECTION EIGHT Hazardous Waste Analysis Plan
8-2
logbook) to each sample. When laboratory results are available, the Hazardous Waste
Program Manager is contacted by email with final lab results.
8.4 RESULTS
When laboratory results indicate hazardous waste characteristics are present, waste will
be processed by DPW-ENRD and transferred to DLADS for storage and disposal per
Section 8, Hazardous Waste Disposal Procedures.
The analytical lab must certify its use of the required EPA test methods and must be able
to provide documentation of quality control and quality assurance procedures. Acceptable
documentation may include compliance with the quality control section of each EPA SW-
846 procedure.
8.5 CHARACTERIZATION FREQUENCY
In general, testing will not be performed on unused hazardous materials that have been
turned in unopened and in their original packaging. Waste characterization of these items
is performed using the item’s physical and chemical characteristics contained in the SDS
as well as standard references to supplement label information.
Waste streams that are generated on a recurring basis are characterized annually or
when changes occur in the process. These annual characterizations and their results will
be reviewed by the Hazardous Waste Program Manager. Hazardous waste profile sheets
for these wastes will be maintained at DPW-ENRD and DLADS and updated as required.
Any non-recurring waste streams will be analyzed if required and profiled as they are
generated prior to acceptance by DLADS. Hazardous waste profile sheets will be updated
as required.
8.6 UNKNOWN WASTES
Unknown wastes are discovered on the installation from time to time. When this occurs,
the contents of these containers or “mystery drums” will be analyzed to determine if they
are a hazardous waste. Based on analytical and physical characteristic results, DPW-
ENRD will make the determination for safely moving these containers to a 90-HWAS if it
is determined to be a hazardous waste. The Fort Rucker Fire Department Hazardous
SECTION EIGHT Hazardous Waste Analysis Plan
8-3
Material Response Team will respond to a “mystery drum or container” in emergencies
or when potential risk is suspected.
8.7 LAND DISPOSAL RESTRICTIONS
In accordance with the LDR regulations in ADEM Administrative Code 335-14-9 / 40 CFR
268, wastes shipped offsite may need to be analyzed to determine whether the waste
meets the applicable LDR treatment standards. If it is known that the wastes do not meet
applicable LDR treatment standards based on process knowledge, no testing will be
performed. Each waste for which a treatment standard has been set will be evaluated for
the applicable parameters in ADEM Administrative Code 335-14-9-.04 / 40 CFR 268.41-
43. All analytical results completed in support of LDR requirements will be retained at
DLADS.
Wastes resulting from facility operations that exceed applicable LDR treatment standards
will be sent offsite to a RCRA-permitted or interim status treatment facility. Applicable
LDR notifications will be supplied with the shipment of waste with the information required
under ADEM Administrative Code 335-14-9-.01(7) / 40 CFR 268.7(a)(1). In addition to
the LDR notification, any additional data for the waste stream (e.g., waste profile sheet,
analytical data) will be available, upon request.
For purposes of the LDR recordkeeping requirement, DLADS is the generator of the
waste that is to be shipped offsite. DLADS personnel will verify the restricted/prohibited
status of each waste stream prior to shipment, since this status is subject to change. The
notification and/or certification forms to be used may be provided by the treatment facility
that receives the waste. Copies of all notices, certification, demonstration, waste analysis
data, and other documentation produced for LDR recordkeeping purposes will be retained
on-site for at least three years from the date the waste was last sent offsite for treatment,
storage, or disposal. The record retention period may be extended during unresolved
enforcement action or at the request of the EPA Regional Administrator.
SECTION EIGHT Hazardous Waste Analysis Plan
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SECTION NINE Hazardous Waste Minimization
9-1
Section 9 Hazardous Waste Minimization
Hazardous waste minimization is the reduction, to the extent feasible, of hazardous waste
that is generated prior to treatment, storage, or disposal of the waste. It includes any
source reduction or recycling activity which results in reduction in volume and/or toxicity
of waste consistent with the general goal of minimizing present and future threats to
human health and the environment. Examples include:
• Chemical substitution - replacement of hazardous chemicals with nonhazardous
or less hazardous chemicals.
• Process or methodology change - development of alternative processes or
methods that use smaller quantities or eliminate the use of hazardous chemicals,
which results in the generation of less waste.
• Segregation of wastes - ensuring that non-hazardous wastes are not contaminated
with hazardous wastes, which increases the total volume of hazardous waste, and
ensuring that otherwise recyclable hazardous wastes remain recyclable because
they are not contaminated by non-hazardous or other hazardous wastes.
• On-site recycle - such as distilling solvents on-site for on-site reutilization.
• Off-site recycle - when possible and economically practical, manifesting hazardous
wastes to off-site recycling companies rather than to disposal or treatment for
disposal.
Commanders and directors will take measures to reduce and minimize the volume and/or
toxicity of hazardous waste generated within their activities whenever practical and in
conformance with the Fort Rucker Pollution Prevention Plan. These measures shall
include implementation of the measures listed above as appropriate and applicable,
including the designation of a pollution prevention coordinator.
9.1 POLLUTION PREVENTION PLAN
Fort Rucker has a Pollution Prevention Plan, which satisfies EPA and ADEM hazardous
waste minimization requirements according to RCRA. The current objective for hazardous
waste reduction uses the CY 2012 hazardous waste quantities as a baseline and
investigates hazardous wastes that are generated on a recurring basis to identify areas
where the amounts of these materials can be reduced and maintained. Personnel have
already investigated or have initiated several pollution prevention projects/efforts. These
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pollution prevention efforts include: replacing the contractor-provided solvent recycle
service with parts washer machines which recycle solvent through a filter-eliminating
liquid replacement; continued use absorbent; digital photographic equipment eliminating
waste silver recovery; and recycling of antifreeze, batteries, and fluorescent bulbs. These
efforts are considered sufficient to allow certification to be made on the manifests that a
waste minimization program is in place.
DPW-ENRD prepares and administers the Pollution Prevention Plan with input from
waste generators. The AR 200-1 requirement that the HWMP describe waste
minimization projects, funds, and savings is satisfied by the Pollution Prevention Plan.
For this reason, the Pollution Prevention Plan is incorporated into this section of the
HWMP by reference, and a copy is available on the Sustainable Fort Rucker website.
9.2 HAZARDOUS MATERIALS
Unused hazardous materials are managed through the Hazardous Material Management
Program (HMMP). A large aim of the HMMP is to reduce the generation of hazardous
waste that results from the use of hazardous materials throughout Fort Rucker. Fort
Rucker Regulation 710-3 establishes the HMMP with a core objective of improving
“logistics and operational mission performance by controlling and reducing the
acquisition, use, handling, and disposal of HM and the generation of HW, consistent with
Army supply chain integration and sustainability objectives.” Additional information about
the HMMP is contained in Section 11 of the Pollution Prevention Plan and on the
Sustainable Fort Rucker website.
As part of the overall HMMP, DPW-ENRD developed USAACE Form 2730, Hazardous
Material Authorization Request, for organizations to use to request addition of a
hazardous material to their authorized use list. This form allows approval from installation
organizations that are involved in hazardous material management and minimization of
waste generation. A copy of this form is located in Appendix N.
9.3 EMS OBJECTIVES AND TARGETS
Each year, the EMS Management Representative and EMS Implementation Team review
and update the installation’s objectives and targets, considering the installation’s
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significant environmental aspects; applicable legal and other requirements; technological
options; relevant financial, operational, and business requirements; and, pollution
prevention opportunity assessments. Because hazardous waste generation is one of the
significant aspects within the Fort Rucker EMS, it is included in the development process.
After identification of an objective relating to hazardous waste, the Hazardous Waste
Program Manager develops a plan that includes the means and timeframe for
achievement utilizing USAACE Form 2724, Objectives and Targets Action Plan. The
Hazardous Waste Program Manager is responsible for tracking progress in achieving the
objective and for reporting to the EMS Implementation Team and the EMS Management
Representative (EMSMR).
The current objective for this program is to reduce hazardous waste disposal by 15% by
CY2020 from a baseline year of CY2012. The Hazardous Waste Program Manager
maintains and updates the USAACE Form 2724, Objectives and Targets Action Plan, to
ensure continued progress in meeting this goal.
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SECTION TEN Installation Waste Stream Summary
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Section 10 Installation Waste Stream Summary
10.1 GENERAL
Hazardous waste, non-hazardous waste, and Universal Waste are handled regularly.
This section is a general summary of the different types of wastes that are generated at
Fort Rucker. Section 12 contains more details regarding the handling and specific
management practices for the most commonly generated waste streams. The Hazardous
Waste Program Manager reviews the profiles and any laboratory analysis prior to signing
any waste manifests to ensure proper waste characterization, management, and
disposal. Copies of all profiles are maintained at DPW-ENRD.
The following major activities generate hazardous waste and non-hazardous waste with
special handling requirements:
• Aviation Maintenance
• Building Maintenance
• Construction Activities
• Fuel/Oil Transfer and Storage
• Ground Vehicle and Equipment Maintenance
• Laboratory Operations
• Medical and Related Research Activities
• Military Training Activities
• Painting Activities
• Photo and X-Ray Activities
• Supply Excess
10.2 HAZARDOUS WASTE
Common hazardous waste streams generated at Fort Rucker are:
• Absorbent materials – contaminated with cadmium, chromium, and/or lead
• Absorbent materials/filters – contaminated with paint
• Paint and thinner
• Abrasive blast media
• Clarus parts washer solvent and filters
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• Fixer/developer
• Caustic cleaning compounds
• Plating shop solids
10.3 NON-HAZARDOUS WASTES
These wastes are not regulated as RCRA hazardous waste, but still require special
handling and disposal actions to ensure that other regulations are not violated. Non-
hazardous wastes may be accumulated and stored in a HWSAP. Although these wastes
are usually not subject to RCRA hazardous waste regulations, they can become a
hazardous waste if they are mixed with or contaminated by a hazardous waste. Common
non-hazardous wastes on Fort Rucker are:
• Asbestos
• Grease
• Latex paint
• Nonflammable adhesives
• Oil, fuel, and grease contaminated rags and debris
• Oil and fuel filters
• Petroleum, Oil, and Lubricant (POL)-contaminated soils and used dry sweep
(except for gasoline)
• Used antifreeze
• Used oil
• Zyglo rinsate
10.4 UNIVERSAL WASTE
Universal wastes regularly managed at Fort Rucker include batteries, fluorescent lamps
(unbroken), mercury containing equipment (thermostats, thermometers), and certain
pesticides. Because of their widespread use in industry and the government, universal
waste can be stored for a longer period of time than hazardous waste and does not
require shipment under a hazardous waste manifest.
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10.5 PROHIBITED ITEMS
Prohibited items are items that must be kept from regular garbage and dumpsters. EOs
and EPOCs should frequently inspect dumpsters in organizational areas and facilitate the
proper disposal of any inappropriate items found in dumpsters. The following items are
not permitted in regular garbage and dumpsters:
• Hazardous waste
• Antifreeze
• POL products
• Used oil and fuel filters
• Contaminated soil
• Paint
• Fluorescent bulbs
• Used dry sweep and absorbents
• Bulk MRE heaters
• Pesticides
• Non-alkaline batteries
• Aerosol cans
• Tires
• Blast media
• Nuclear, biological, and chemical (NBC) items
• Solvent and filters
• Hazardous materials
• Ammunition-related items (anything issued by the ammunition supply point [ASP])
• Used/dirty rags
10.6 POLYCHLORINATED BIPHENYLS
Polychlorinated biphenyls (PCBs) are synthetic compounds used widely as a dielectric
fluid in transformers and capacitors, in light ballasts, and for other insulating uses prior to
1978. PCBs are regulated by the Toxic Substances Control Act (TSCA) and under 40
CFR 761. TSCA requires that all items manufactured after 1978 be labeled as to whether
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the item is PCB or non-PCB containing. When no identifying label is present, assume that
it contains PCBs and contact the PCB program managed within DPW-ENRD. Fort Rucker
has no known remaining PCB items in service or storage on the installation. However,
some items, such as ballasts, may be discovered during maintenance of older facilities.
Organizations should contact DPW-ENRD for further guidance if any potential PCB
containing items are identified. Copies of the PCB logs are maintained in DPW-ENRD.
10.7 REGULATED MEDICAL WASTE (RMW)
Regulated medical waste (RMW) is waste that is potentially capable of causing disease
in humans and may pose a health risk to individuals, the community or both, if not handled
or treated properly. All medical waste is managed through Lyster Army Health Clinic.
RMW includes the following:
• All sharps, used and unused
• Free flowing blood or blood products including blood specimens, vials and blood
in bags
• Any item saturated or dripping with blood or body fluids
• Pathological specimens
• Microbiological waste such as cultures, stocks, and vaccines
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Section 11 Waste Stream Management
The following sections describe specific management procedures for hazardous wastes,
universal wastes, and non-hazardous wastes that are commonly encountered during daily
operations at Fort Rucker.
11.1 ABSORBENT MATERIALS
11.1.1 Continued Use Absorbents The absorbent continued use program is designed to be a closed-loop system where
used absorbent materials are returned to the vendor for cleaning and returned to the
generating facility for reuse. Before the absorbent continued use program was
implemented, maintenance personnel used disposable absorbent items in daily
maintenance activities. These materials were characterized as hazardous waste due to
the presence of cadmium, a toxic metal commonly used in aircraft and aircraft
components. DPW-ENRD petitioned ADEM for approval of the program, which was
granted on 27 April 2005. Organizations should consult EMS-WI-SW009, Absorbent
Continued Use Program to ensure proper implementation of the program. A copy of this
work instruction is located in Appendix O.
The following items are available for use through the program:
• Pads
• Socks
• Wipes
• Gloves
• Mopheads
• Pillows
After the items have been used, personnel place them into designated containers located
in the operational area. These containers are then collected by the continued use
absorbents vendor for laundering. After laundering, the vendor returns the material to Fort
Rucker for reuse.
Organizations should use USAACE Form 2732, Continued Use Absorbents Tracking
Document, to record turn-in and receipt of the absorbents and provide DPW-ENRD with
drum identification numbers, deliver/pickup date, total weight and number of drums
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received and returned using USAACE Form 2732, Continued Use Absorbents Tracking
Document, no later than 7 days after delivery or pickup.
A copy of this form is located in Appendix P.
11.1.2 Disposable Absorbents Absorbents, including paper or cloth wipes, rags, filters, spill pads, and booms that are
not part of the continued use program and that are contaminated with hazardous
materials, including paints and other materials, must be collected and managed as a
hazardous waste in a HWSAP in accordance with Section 5 unless sampling has been
completed to document otherwise.
Oil and fuel (except motor gasoline [MOGAS]) contaminated absorbents are not
hazardous waste if no other product has contaminated them. However, these used
absorbents should be collected separately in a container labeled “ABSORBENTS
CONTAMINATED WITH OIL” and turned in to the 90-HWAS for proper disposal as a non-
regulated waste. Oil and fuel (except MOGAS) contaminated rags may be laundered if
not saturated or may be disposed through the 90-HWAS. Materials contaminated with
MOGAS should be collected and managed in a HWSAP in accordance with the
procedures in Section 5.
11.1.3 Sweeping Compound Sweeping compound, including oil-dry, sand, or vermiculite, saturated or contaminated
with a hazardous substance, must be managed as a hazardous waste in a HWSAP in
accordance with Section 5. Sweeping compound contaminated with MOGAS should be
managed as a hazardous waste in a HWSAP in accordance with the procedures in
Section 5. Sweeping compound, saturated or contaminated with oil or fuel (except
MOGAS), should be managed as a non-regulated waste and turned in to the 90-HWAS
for disposal.
POL-contaminated dry sweep and soil must never be thrown in a dumpster, trash can, or
landfill. Dry sweep should be collected in a container and labeled as “USED DRY
SWEEP.” The container must have a lid and be kept closed at all times. Contaminated
dry sweep and soil are turned in to the main 90-HWAS. All soil and dry sweep must be
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free of debris (i.e., plastic bags, buckets, cans). This material is then disposed through a
DLADS contract.
11.2 ADHESIVES
Adhesives are used during maintenance activities for aircraft and ground vehicles.
Adhesives that are two-part mixtures that are chemically cured or air cured prior to use
are hazardous wastes due to their flashpoint. Small amounts of unused adhesive, stir
sticks, and mixing cups with adhesive residue may be thrown into the trash after drying.
11.3 AEROSOL CONTAINERS
All aerosol containers, including empty and malfunctioning containers, must be turned in
to the HMCC for proper management and/or disposal. Generators should collect aerosol
cans that are no longer being used in the operational area in a container marked “HazMat
for Return to HMCC.” The HMCC will make the determination of aerosol serviceability.
Containers with product may be put into the Free Issue Program. Aerosols that are not
functioning or empty will be punctured and processed as scrap metal by the HMCC.
Appendix F contains ADEM guidance on management of used aerosol cans.
11.4 ANTIFREEZE
Antifreeze (ethylene glycol, or the less toxic propylene glycol) should be collected in an
approved plastic container that is labeled “USED ANTIFREEZE” and that is kept closed
when not adding or removing used material. The container should have secondary
containment to prevent potential spills from contaminating stormwater. Organizations
should ensure that used oil is not mixed with the antifreeze in order to ensure the
antifreeze can be recycled.
The used antifreeze container should be turned in to the centralized 90-HWAS for
recycling. Although used oil and antifreeze are not classified as hazardous wastes, they
should be handled with the same care as hazardous wastes, since spills of these
substances require response under the Fort Rucker ISCP.
Antifreeze should never be poured into a storm drain or in an oil-water separator.
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11.5 ASBESTOS
Asbestos containing material may be generated as part of renovation and demolition
projects being conducted on the installation. Samples of any suspected asbestos
containing material (ACM) are sent to a lab for verification. If ACM is generated for
disposal, the material should be collected in accordance with ADEM regulations. ACM
may be disposed of in any permitted landfill in Alabama with written approval from ADEM,
following the special waste provisions found in ADEM regulations at ADEM Administrative
Code 335-13-4- .26(2).
11.6 ASPHALT AND RELATED WASTES
Asphalt is used as a paving material on most installation roads. In general, contractors
that perform road maintenance activities should dispose of all waste that is generated as
a part of their activities. The contractor should coordinate with DPW-ENRD regarding
these wastes to determine proper management procedures. Asphalt contractors should
always use all material for its intended purpose to the greatest extent possible.
The DPW Roads and Grounds Section also uses an asphalt emulsion when cleaning out
asphalt residue in vehicles that are used for road repair activities. This residue from
cleaning operations should be containerized in approved containers and managed in a
HWSAP in accordance with the procedures contained in Section 5.
11.7 BATTERIES
11.7.1 General Requirements Fort Rucker generates batteries from military-specific applications, such as radios,
vehicles (both military and civilian), and aviation equipment, and from general operations
such as computers and cell phones. New batteries must be stored in their original
packaging in a cool, dry location. Batteries that have been removed from their original
packaging must be clearly segregated from new batteries, including batteries considered
used and in use.
While accumulating used batteries for turn-in, they must be placed in a properly labeled,
DOT approved container with a closing lid; or, for larger lead-acid batteries, stored in
covered areas on pallets or in a covered spill containment pallet. Batteries should not be
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stored directly on the ground or the floor. All batteries must be stored with consideration
for potential compatibility issues. Water reactive batteries should be stored a minimum of
six inches above the floor or ground.
Batteries of any type can be dangerous, especially if swollen, broken, leaking, or
improperly vented. Leaking or damaged batteries (dry cell or sealed) must be segregated
from intact used batteries inside the container by placing the leaking or damaged battery
in a sealed plastic bag or wrapped with plastic and sealed using tape. Lead-acid batteries
that are leaking or are damaged (e.g., cracked case) will be accumulated in a HWSAP
for disposal as hazardous waste.
Organizations and activities must not accumulate more batteries than are manageable.
The organization and activities should consider such factors as storage space, usage
rates, packaging costs, man-hours, and safety when accumulating batteries.
Any quantity of batteries may be stored at one time, but Fort Rucker organizations are
encouraged to transfer the batteries to the HMCC prior to accumulation of a large quantity.
Organizations must transfer universal waste batteries to the HMCC or 90-HWAS within
six months of the accumulation start date to ensure sufficient time remains to allow for
processing for disposal.
Organizations should not discharge lithium sulfur dioxide (LiSO2) batteries on Fort
Rucker.
Used or unusable batteries such as Lithium, Nickel-Cadmium (NiCd), Mercuric-Oxide
(button and other), Nickel Metal Hydride (NiMH), Silver Oxide, Silver-Zinc, Zinc-Carbon,
and Zinc Air batteries will be managed as Universal Waste. Containers and/or areas used
for storing universal waste batteries must be labeled with the words “UNIVERSAL
WASTE BATTERIES” and the date that the first battery was placed in the container
(accumulation start date). Universal waste batteries should have their connectors taped,
and the batteries should be placed in an approved container. Like batteries are
containerized together. These containers must be stored as universal waste and turned
in to the HMCC, Bldg 1315 for recycling.
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Used single-use dry cell Alkaline and Carbon-Zinc batteries (e.g., 9-volt, D, C, AA, AAA,
alkaline button) are managed as Non-Hazardous Waste.
EMS-WI-SW002, Used Battery Management, in Appendix Q, provides guidance for
proper labels, signs, storage, and turn-in procedures for used batteries.
11.7.2 Small Rechargeable Batteries Fort Rucker has two programs for recycling small rechargeable batteries, such as NiCd,
lithium ion, and NiMH batteries.
The main program that Fort Rucker is working with is Call2Recycle. This nonprofit
organization offers consumers and retailers in the United States and Canada simple ways
to recycle old phones and rechargeable batteries. Call2Recycle drop-boxes are located
in the HMCC.
Fort Rucker has also partnered with Cell Phones for Soldiers, which works to turn old cell
phones into more than 12 million minutes of prepaid calling cards for U.S. troops stationed
overseas. Drop off locations on Fort Rucker are at the Recycling Center (Building 9322),
DPW-ENRD office, and the HMCC.
11.7.3 Lead Acid Batteries Fort Rucker participates in a battery program that is a one-for-one exchange of new and
unserviceable batteries for lead-acid batteries. A contractor supplies new batteries to
organizations and picks up any used batteries that have been collected. The
unserviceable batteries are handled and transported by the contractor to a battery
recycler for recycling. The contractor takes the entire battery (including the electrolyte
solution). If the contractor does not have a particular facility on the pickup route, the
organization may turn in their used lead-acid batteries to the HMCC.
Any batteries with a cracked case cannot be returned to the vendor as part of this
program. These batteries should be accumulated in a HWSAP and turned in to the 90-
HWAS for disposal as hazardous waste.
Draining batteries before collection is not necessary. Both new and used batteries should
be stored in covered areas on pallets or in a covered spill containment pallet. These
batteries do not need to be labeled as universal waste.
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Although the batteries are not managed as universal waste, the organization should not
accumulate the batteries for an extended period of time. Organizations should implement
a method to demonstrate how long the batteries have been stored between shipments.
11.8 BATTERY FLUID
Historically, battery shops have been used for maintaining wet cell batteries. Battery
shops are no longer major sources of hazardous waste generation. The operations in
these areas have been scaled down significantly due to an Army-wide implementation of
a closed-loop battery program. Wastes that are generated from these processes, such as
electrolyte solutions, are usually corrosive and must be disposed as hazardous waste.
Personnel should collect these wastes in an approved non-metal container or a metal
container with an appropriate liner in a HWSAP in accordance with the procedures
described in Section 5. Any personnel generating these types of wastes should
coordinate with DPW-ENRD to ensure that these wastes are properly containerized due
to the corrosive nature of the waste. Any cracked batteries must also be collected in a
HWSAP in accordance with the procedures in Section 5.
11.9 BLAST MEDIA
Blast media is used prior to painting as well as to ensure complete cleaning of parts during
specialized maintenance activities. Blast media is used in a blasting booth that reuses the
media until it is no longer useful for blasting purposes due to having particles that are too
fine to be effective. Personnel at the blast facility should check the quality of the blast
media that is removed by the filtration system to determine whether it can be reused. If
the blast media can be used again, it should be added to the blast media that is supplied
to the booth. Blast media that is no longer effective must be stored and managed as a
hazardous waste in a HWSAP in accordance with the procedures described in Section 5.
Blast media is usually contaminated with metal and paint particles, which cause it to be
hazardous waste. Filters used during blasting operations may also be hazardous due to
filtration of the same metal and paint particles contained in the blast media from the air.
Prior to disposal of these items, organizations should contact DPW-ENRD to verify the
waste classification.
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11.10 BOILER TREATMENT
Use of boiler treatment chemicals is periodically required to ensure proper operation of
equipment and to remove and prevent mineral buildup. Various types of corrosive
chemicals are used to remove buildup of scale during routine maintenance of these
systems. The heat plant operators should coordinate with DPW-ENRD when generation
of a waste results from these operations. In general, the materials are used completely
during the cleaning process. However, when a waste is generated, the waste should be
collected in an approved container designed for corrosive materials and accumulated in
a HWSAP in accordance with the procedures described in Section 5.
11.11 CORROSION PREVENTION AND REMOVAL
Corrosion is a large maintenance concern for Army vehicles and equipment. In order to
minimize the costs associated with removing corrosion and replacing corroded
equipment, the Army has implemented aggressive corrosion control programs. Part of
these programs involves the application of various compounds designed to prevent and
remove corrosion on all types of military equipment. Waste that is generated as a result
of these activities includes various corrosion preventative and preservative coatings used
to prevent rust on materials and equipment as well as corrosion removing compounds.
These wastes are often classified as hazardous waste and should be accumulated in an
approved container at a HWSAP in accordance with Section 5.
11.12 CYLINDERS
Types of cylinders disposed in the past include ammonia, oxygen, nitrogen, acetylene,
butane, propane, engine starting fluid (ether), and fire extinguishers. When disposing of
cylinders, the organization should coordinate with DPW-ENRD regarding the types,
quantities, and locations of the cylinders, preparing the necessary disposal
documentation, and coordinating with DLADS for their disposal. When possible, these
cylinders should be returned to the vendor for reuse or recycling rather than being
disposed through DLADS.
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Quick Start ether cylinders should be returned to the vendor rather than disposed as
hazardous waste. Organizations are required to use this program for these cylinders
because of the high cost for disposal through DLADS.
When refrigerant cylinders (non-refillable) are empty, personnel should punch a hole in
each cylinder. The cylinders should be crushed and turned in to DLADS for scrap metal
recycling.
11.13 EMPTY CONTAINERS
In general, containers are considered empty when there is less than one inch of residue
on the bottom or less than three percent by weight remaining in the container. Empty
containers must be kept closed at all times.
Empty containers that are to be turned in to DLADS must be properly marked with the
word "EMPTY" and DOT shipping name and UN/NA ID number of previous contents.
Empty containers which previously held hazardous materials bearing a DOT hazardous
warning label, such as flammable liquid, corrosive, etc., must continue to bear this label
unless cleaned and purged of all vapors. Containers must be completely free of holes
and have all caps, lids, plugs, etc., affixed. Empty containers that are going to be reused
by the organization must be marked “EMPTY” and with the previous contents. Containers
must be in good condition for reuse. If the product came through the HMCC, approval
must be received from the HMCC before reuse of the empty container.
Empty containers which have contained hazardous materials or hazardous waste, other
than acutely hazardous waste listed in ADEM Rule 335-14-2-.04(2), (3), and (4)(e), and
which are over five gallons, will be drained to less than one inch of residue; marked
“EMPTY” and with the chemical name of the original contents; and may be turned in to
the HMCC. All containers must be closed and non-leaking. Some containers, such as
small alcohol or oil containers, may be drained and disposed in a dumpster in the
organizational area. The Hazardous Waste Program Manager will provide guidance for
specific containers upon request.
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11.14 FUEL
MOGAS is highly ignitable and must not be mixed with any other type of fuel.
Contaminated MOGAS should be stored as a hazardous waste in a HWSAP managed in
accordance with the procedures described in Section 5. MOGAS must always be stored
in a grounded, approved metal container.
F24, diesel and kerosene contaminated with water must be collected in a metal 55-gallon
drum or an aboveground storage tank. The drum or tank should be labeled with the
contents of the container and have appropriate secondary containment. MOGAS, oil,
antifreeze, and solvents should not be mixed with the fuel. Mixing these materials may
create a hazardous waste that cannot be recycled or reused. When the container is
approximately 75 percent full, the organization should contact DPW-ENRD to schedule
removal of the fuel.
11.15 FUEL FILTERS
Once used fuel filters are removed from a vehicle, the residual fuel should be drained into
an approved metal container designated for collection of contaminated fuel. The filters
are not required to be drained for any set length of time, but should be drained long
enough to remove free flowing liquid. Organization personnel must not leave the fuel
filters unattended while draining.
For used MOGAS filters, after draining, the filters must be stored as hazardous waste in
an approved metal container in a HWSAP and managed in accordance with the
procedures described in Section 5.
For all used F24 or diesel filters, crush filters in a suitable machine so that the scrap metal
can be recycled and the used fuel captured and transferred into the used fuel
accumulation container or tank.
The container used to collect the drained fuel is managed according to the procedures
described in Section 11.14. Additional details about management of these filters may be
found in EMS-WI-SW007, Management of Used Oil and Fuel Filters, a copy of which is
located in Appendix R.
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11.16 GREASE AND RELATED ITEMS
Grease, Automotive and Aviation (GAA) is used in many applications for vehicle and
aircraft maintenance throughout Fort Rucker. Every effort should be made to completely
use all product in containers before opening a new container or disposing open
containers. Any waste GAA or other grease is stored in an approved, labeled container
and turned in to the HMCC for disposal. This waste is generally not a HW, but it is
managed through DPW-ENRD due to restrictions on disposal of this material in landfills.
11.17 IMAGE INTENSIFIER TUBES
Image intensifier tubes that are part of the night vision devices must be demilitarized
before they can be disposed. Fort Rucker organizations may demilitarize the intensifier
tubes at the installation in accordance with published Army guidance. Both demilitarized
and cracked or damaged image intensifiers should be collected in a HWSAP and
disposed as hazardous waste in accordance with the procedures in Section 5.
11.18 INSECT REPELLANT
Permethrin insect repellant is used in military applications and comes in either an aerosol
can or an application kit consisting of a vial of permethrin with a plastic bag. Prior to
collecting for disposal, organizations should coordinate with other installation
organizations to ensure that they do not have a need for these items. The insect repellant
is used during most training exercises and during deployments. When these items must
be disposed, both the aerosol and vial forms of the insect repellant should be managed
as hazardous waste. They should be accumulated separately in approved containers in
a HWSAP in accordance with the procedures contained in Section 5.
11.19 MEDICAL ACTIVITIES
All regulated medical waste (RMW) must be managed through Lyster Army Health Clinic.
All RMW is incinerated by a contractor at an off-site facility. RMW generated on Fort
Rucker should be managed in accordance with local requirements. Organizations should
contact the Department of Preventive Medicine at 334-255-7012 for additional information
and guidance.
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11.20 MERCURY-CONTAINING LAMPS
Fluorescent and high intensity discharge (HID) lamps (bulbs) contain low levels of
mercury, which fail the TCLP analysis for an item to be disposed of in the municipal
landfill. Used lamps are to be collected in a box, marked with the words “UNIVERSAL
WASTE” and “Used Lamps” and with the date the first lamp was placed in the box. The
box must be kept closed at all times except when adding or removing bulbs. All
fluorescent and HID lamps, including mercury vapor, metal halide, and high-pressure
sodium lamps, must be managed as universal waste, as described in EMS-WI-SW003,
Used Lamps Management. A copy of this work instruction is located in Appendix S.
Broken lamps must be collected, doubled-bagged in plastic bags, and containerized in
accordance with the procedures in EMS-WI-SW003, Used Lamps Management, a copy
of which is located in Appendix S. The collected waste should be managed as a
hazardous waste in a HWSAP or 90-HWAS in accordance with the procedures in Section
5 and 6. Vacuums/HEPA vacs will not be used to clean up broken lamp spill residue
because the mercury vapor may be released when heated during subsequent uses of the
equipment.
11.21 MERCURY-CONTAINING EQUIPMENT
Mercury-containing equipment means a device or part of a device (including thermostats,
but excluding batteries and lamps) that contains elemental mercury integral to its function.
Thermostats and thermometers that contain mercury are the most common types of this
equipment found on Fort Rucker.
Organizations manage these items as a universal waste when they are no longer usable.
The items are stored in a closed container that is labeled “UNIVERSAL WASTE -
MERCURY CONTAINING EQUIPMENT.” The date that the items were first placed in the
container is also indicated. Because the thermostats and thermometers can be easily
broken, care must be taken when packaging this waste. Organizations should obtain
vermiculite to package these items in a manner to prevent accidental breakage. When
the container is full, the organization should turn in the waste to the HMCC for disposal
through the DLADS contractor.
SECTION ELEVEN Waste Stream Management
11-13
11.22 MILITARY MUNITIONS
Military munitions must be handled and stored responsibly to minimize the potential for
harm to human health and the environment. All military munitions should be stored in
accordance with DOD 6055.9-STD, which establishes explosives safety standards.
Waste military munitions (WMM) must be managed in accordance with the Munitions Rule
(ADEM Administrative Code 335-14-7-.13 / 40 CFR 266 Subpart M), the Munitions Rule
Implementation Policy (MRIP), and any applicable federal, state, or local regulations. In
the event such regulations conflict with DOD 6055.9-STD, Fort Rucker will follow DOD
6055.9-STD for purposes of explosive safety until the conflict is resolved.
Military munitions and related items must be certified as inert prior to disposal. This
certification must be performed by qualified personnel as described in the MRIP. The
organization generating waste is responsible for ensuring that the items are certified inert
prior to being turned in. These items should not be accumulated in organization areas; all
military munitions should be turned in to the ASP for proper management.
11.23 NUCLEAR, BIOLOGICAL, CHEMICAL (NBC) ITEMS
Some NBC items require disposal as a hazardous waste when they can no longer be
used for their intended purpose. The waste determination should be made by DPW-
ENRD personnel prior to accumulation in the organization area. A HWSAP should not be
established in the NBC rooms in organization areas if these items are determined to be
a hazardous waste. Items that are generally classified as hazardous waste include
protective mask filters, M72A2 chemical agent ID kits, M256A1 chemical agent detector
kits, M229 chemical agent alarm refill kit, M258A1 decontamination kit, DS2 decon
solution, and STB.
11.24 PAINT RELATED ITEMS
11.24.1 Latex Paint Latex paint that has expired or is not needed is stored in an approved, labeled container
and turned in to the HMCC for reissue or disposal through DLADS. Latex paint is generally
not a hazardous waste. Paint cans from latex paint may be placed in a regular dumpster
after all of the paint has been used and the inside of the container is dry.
SECTION ELEVEN Waste Stream Management
11-14
11.24.2 Hazardous Waste Paint and Thinner Unusable enamel, Chemical Agent Resistant Coating (CARC) paint and leftover paint
thinner must be managed as a hazardous waste in a HWSAP in accordance with the
procedures described in Section 5. CARC paints are particularly hazardous and may
degrade while in the can and become unusable. For example, CARC Component "B"
should be clear to pale yellow. If it thickens and appears crystalline in consistency,
organizational personnel should reseal it and return it to the HMCC.
11.24.3 Paint Containers In general, all containers of unusable or outdated paint must be turned in to the HMCC,
Bldg 1315. Partially used cans of paint must be returned to the HMCC. Paint cans should
be managed in a manner to meet the RCRA definition of empty as specified in 335-14-2-
.01(7)(b)(1) / 40 CFR 261.7(b)(1). Any paint in cans should be removed using practices
commonly employed for emptying the containers, primarily pouring. Also, the cans should
have less than one inch or three percent by weight of the container capacity of paint
remaining. Paint cans from other types of paint must be turned in to the HMCC for proper
disposal.
11.24.4 Paint Solids Paint solids are generated at most paint booths. These solids include filters generated at
paint booths, plastic sheeting that catches overspray in the paint booths, dried paint
scraped from surfaces, and any other items that contain dried paint. Paint solids that may
contain lead based paint (LBP) may also be generated during renovation and demolition
projects. Any solids determined to be hazardous waste should be managed in a HWSAP
in accordance with the guidelines in Section 5. DPW-ENRD will provide management
guidance based on the type of paint solids that are generated.
11.25 PARTS WASHER SOLVENT AND FILTERS
Parts washers are used in maintenance operations for ground vehicles, aircraft, and
ground and aviation equipment on the installation. As a result of their widespread use,
solvent wastes have been drastically reduced due to implementation of multiple waste
minimization initiatives. Parts washers on Fort Rucker are Clarus machines that are
owned by the installation and serviced by personnel with the HMCC. Maintenance is
SECTION ELEVEN Waste Stream Management
11-15
performed by the facility maintenance contractor. Personnel must prevent contamination
of parts washer solvent by prohibited materials, such as paints. Contamination of the
solvent in installation owned parts washers will prevent this solvent from being filtered
and reused. The Clarus machines have built in filtration systems that extend the life of the
solvent. DPW-ENRD also has an external filtration machine that is being used to further
filter solvent used for ground equipment. This initiative may be expanded to include
aviation equipment after additional analysis is completed on the filtered solvent.
Solvent and filters generated by some organizations has been determined to be
nonhazardous through laboratory analysis. DPW-ENRD maintains records of the analysis
results and will ensure the waste from these organizations is appropriately disposed as
nonhazardous waste. The HMCC is responsible for changing all solvent and is
responsible for ensuring its proper management. Organizations with parts washers do not
generally have a HWSAP established for used parts washer solvent.
11.26 PESTICIDES, HERBICIDES, AND RODENTICIDES
Pesticide use is regulated under the Federal Insecticide, Fungicide, and Rodenticide Act
(FIFRA). Because the use and application of pesticides is strongly regulated, Fort Rucker
has a contract that covers most pesticide applications. Organizations are not permitted to
have large quantities of pesticides, herbicides, insecticides, and rodenticides stored in
their areas. Any waste generated by contractors should be properly containerized and
manifested when it leaves the installation. A DPW-ENRD representative must sign all
manifests of contractor-generated waste prior to the waste being shipped off-site.
Some pesticides may be hazardous due to their toxicity. DPW-ENRD provides additional
guidance on proper management of these items as they are generated on a case-by-case
basis. Aerosol pesticides, herbicides, and rodenticides should be managed as described
in the aerosol section above.
Pesticides that meet the definition of hazardous waste may be managed as universal
waste if they are recalled pesticides or stocks of unused pesticides collected as part of a
waste pesticide collection program, as described in ADEM Administrative Code 335-14-
11-.01(3) / 40 CFR 273.3. DPW-ENRD will make a determination of the management
method on a case-by-case basis. Any waste that is generated by organizations should be
SECTION ELEVEN Waste Stream Management
11-16
collected in an approved container in a HWSAP managed in accordance with Section 5
unless otherwise directed by DPW-ENRD.
11.27 PHOTO PROCESSING CHEMICALS
Some photographic waste solutions are hazardous due to corrosivity. Other photographic
waste solutions are not classified as hazardous waste due to the precious metal
exemption. Photographic waste solutions classified as hazardous waste are stored in
approved plastic containers in a HWSAP managed in accordance with the procedures
described in Section 5. Recyclable materials from which precious metals (i.e., silver) are
recovered are exempt from full hazardous waste regulation; however these materials are
subject to administrative requirements such as using manifests and complying with LDR
notification requirements.
11.28 PLATING SHOP WASTES
Plating solutions and solids contaminated with the plating solutions are generated at the
Cadmium Plating Shop at AMSS (Building 1001). Both the liquids and solids from each
shop should be managed in a HWSAP. The liquid waste and the solids waste should be
accumulated in separate 55-gallon drums in the plating shop. If necessary, the liquid
waste drum may be fitted with a funnel for adding waste to the drum. However, the funnel
must be attached securely to the drum bung and equipped with a closing mechanism that
will prevent spilling in the event that the drum is overturned.
11.29 POLYCHLORINATED BIPHENYLS
Fort Rucker is not aware of any PCB items still in use on the installation. Although all
known PCB items have been disposed, the potential exists for additional items to be
discovered due to the large area covered by the installation. If any items containing PCBs
are discovered, the items will be managed in accordance with TSCA and the guidelines
of this section.
PCB-contaminated (more than 50 ppm) oils, solid waste, soils, and rags contaminated
with fluids require disposal as TSCA regulated waste. All materials commonly
manufactured with PCBs in the past are still considered to contain PCBs unless testing
is feasible, or unless the equipment or item is marked by the manufacturer to indicate “no
SECTION ELEVEN Waste Stream Management
11-17
PCBs” or “non-PCB.” The main source of PCBs is electrical transformers. When
transformers are taken out of service, or when other suspected PCB-containing items are
encountered, a screening test is performed to determine if the items are contaminated
with more than 50 ppm PCBs. Organizations should contact DPW-ENRD to arrange for
the testing.
PCB-contaminated wastes should be turned in to the HMCC for storage and disposal.
Items that are known to contain above 50 ppm PCB are manifested and removed from
the HMCC by a DLADS service contractor. PCBs are regulated under TSCA, and many
PCB management requirements differ from hazardous waste management requirements.
TSCA (40 CFR 700-789) should be consulted to ensure compliance with management
requirements.
A DLADS contractor accepts suspected or known transformers for disposal as either PCB
contaminated (contains 50 to 500 ppm PCBs) or PCB transformers (contains 500 ppm or
greater PCBs). Light ballasts or capacitors manufactured prior to 1978 are also generally
suspected to be PCB-contaminated, and must be disposed through DLADS. Because it
is neither practical nor cost effective to perform testing on these items, all items not
permanently stamped or marked as “non-PCB” should also be disposed of as PCB-
contaminated through DLADS as a best management practice.
All PCB transformers or other PCB wastes will be stored in a secure area, with adequate
secondary containment, and with proper markings (a PCB label is used when required).
Documentation is maintained on all PCB items in storage. PCB wastes must be in DOT
or UN containers. Transformers, which are generally too large for overpacks, must be
sealed with no leaks. PCB labels must be placed on all PCB containers as well as the
applicable DOT shipping label (Class 9 Miscellaneous, as required by 49 CFR 170-189).
All PCB wastes will be disposed through DLADS using a standard DD Form 1348-1A,
Issue Release/Receipt Document (Appendix H).
11.30 PROCESS PARTICULATES
The aviation maintenance contractor uses Clayton tools for sanding and preparing
various metal pieces as part of processes in multiple facilities, mainly in sheet metal and
paint shops. The Clayton tools are equipped with high efficiency particulate air (HEPA)
SECTION ELEVEN Waste Stream Management
11-18
filters and a collection chamber for particulates that are removed during their processes.
The dust and filters generated from these processes should be managed in a HWSAP in
accordance with the procedures in Section 5.
11.31 RATION HEATERS
Organizations should use/activate field ration heaters (FRH) with food during training in
the field. The used FRH can then be placed with regular trash. Unactivated FRH can also
be placed in regular trash containers as long as they are placed individually into the trash
receptacles. Consolidating and discarding multiple FRH is not allowed in regular waste
containers; these must be managed as hazardous waste in a HWSAP in accordance with
the procedures described in Section 5.
Solid fuel used for cooking food, boiling water, or heating MREs, such as trioxane fuel
bars, are lit and burn for several minutes to heat items in the field. These fuel bars are not
as commonly used as the flameless heaters due to safety concerns. Organizations should
completely use the fuel bars for their intended purpose to help prevent generation of this
waste stream. Any solid fuel sources such as this should be accumulated in a HWSAP in
an approved container as described in Section 5.
11.32 SCRAP ITEMS
11.32.1 Scrap Metal All scrap metal should be accumulated in designated areas within the organization’s
operational areas. Any type of scrap metal should be turned in to the Recycling Center
(Building 9322) for recycling. Lead weights may also be recycled as a scrap metal. Scrap
metal should be turned in to the Recycling Center at the roll-off container located behind
the building.
11.32.2 Items Requiring Special Handling The following items cannot be processed as scrap and must be turned in on a separate
DD Form 1348-1A as hazardous or regulated waste since they may contain or be
contaminated with lead deposits, PCBs, or asbestos:
• Fuel tanks
• Asbestos brake shoes, gaskets and clutch plates
SECTION ELEVEN Waste Stream Management
11-19
• Undrained hydraulic rams, gas cylinders, and shock absorbers
11.33 SOLDER
Lead and silver solder are used in electronics and avionics shops on the installation to
properly maintain and repair this equipment. Waste solder is collected at each location
and recycled. Call DPW-ENRD recycling program manager who will contact the recycler
who will come and pick it up.
11.34 TONER
Toner is generated during printing operations across the installation. Many of the toner
cartridges that are used in office-type printers are able to be returned to the vendor for
recycling free of charge. Personnel should save toner cartridge shipping boxes and use
them to return the cartridges to the vendor when possible. Toner cartridges that are not
returned to the vendor by the organization should be turned in to the HMCC or the
Recycling Center for recycling.
11.35 USED OIL
Organizations collect used oil (motor oil, hydraulic fluid, brake fluid, transmission fluid,
diesel, and F24) for recycling through a contract administered by the Recycling Center.
For information on collection points and times, contact DPW-ENRD. Containers of used
oil will be marked "USED OIL" and a sign posted stating "Used Oil Only".
All containers must be closed in order to meet ADEM used oil requirements. Any container
equipped with a funnel must have a method to keep the funnel closed that would prevent
a release in the event that the container falls over.
All used oil containers that are 55-gallons or larger are subject to inspection requirements
contained in the SPCC Plan. The SPCC Plan requires weekly inspections of these
containers using USAACE Form 2711, SPCC Container Inspection Checklist. A copy of
this inspection checklist is included in Appendix E.
Used cooking oil is accumulated separately from used petroleum oil in accordance with
the requirements in EMS-WI-SW008, Used Cooking Oil Management.
SECTION ELEVEN Waste Stream Management
11-20
11.36 USED OIL FILTERS
Personnel managing metal used oil filters from vehicles where the filter is one quart or
smaller (i.e., spin-on filters) may return the used oil filters to the HMCC directly or place
the used oil filters in designated blue totes for pick up by HMCC delivery personnel. Metal
filters are then drained, crushed and recycled by the generating HMCC. Used oil filters that
have not been punctured or crushed or are being accumulated prior to crushing must be
in containers marked “USED OIL FILTERS”. Containers must be closed except when
adding or removing the filters. Used oil filters must be properly drained then punctured in
the dome and crushed in a suitable machine before placing the filter into collection
containers for scrap metal recycling. Non-metal filters (from all engines except gasoline)
must be drained of free flowing liquid, and then may be disposed in regular trash. All
containers or tanks used to collect and store the used oil drained from filters must be
marked “Used Oil” and managed per current procedures for used oil management.
Additional details about managing used oil filters may be found in EMS-WI-SW007,
Management of Used Oil and Fuel Filters, a copy of which is located in Appendix R.
11.37 WASHRACK SAND/SOIL
Washracks should be managed in accordance with Fort Rucker Regulation 420-14. In the
event that an organization suspects that washrack soil or sand residue contains
hazardous materials, the organization should contact DPW-ENRD and request an
inspection of the soil. DPW-ENRD will provide guidance for the disposal on a case-by-
case basis. Organizations should never allow more than one foot of soil/residue to
accumulate in the traps. This precaution will prevent large volumes of the soil/residue
from possibly becoming contaminated.
11.38 WEAPONS CLEANING MATERIALS
Used weapons cleaning materials include bore patches, Q-tips, and pipe cleaners used
to clean weapons. Personnel should use approved weapon cleaner to clean weapons.
Used cleaning materials should be collected by the organization armorer and stored as
hazardous waste in an approved container in a HWSAP managed in accordance with the
procedures described in Section 5.
SECTION ELEVEN Waste Stream Management
11-21
11.39 X-RAY RINSE WATER
Water that is generated as a result of the x-ray developing process is collected for
disposal as hazardous waste for silver contamination. This waste should be managed in
a HWSAP in accordance with the procedures in Section 5.
11.40 ZYGLO RINSATE
Zylgo is used as part of the non-destructive investigation (NDI) process for aircraft
maintenance and repair. The rinsate from this process is a non-hazardous waste that
must be accumulated in a drum for disposal through DLADS. The rinsate should not be
disposed through the wastewater system due to slightly corrosive nature of the waste.
SECTION ELEVEN Waste Stream Management
11-22
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SECTION TWELVE Spill Response Procedures
12-1
Section 12 Spill Response Procedures
12.1 GENERAL
A spill is the accidental spilling, leaking, pumping, emitting, discharging, emptying or
dumping of hazardous wastes or materials into or on any land or water. All spills are
serious incidents as even a small spill can contaminate millions of gallons of drinking
water. Every soldier, civilian, and contractor is responsible for proper handling of
hazardous materials and wastes, and cleaning any minor spills. The pouring of any
hazardous material on the ground or in a storm drain is illegal and punishable under
civilian laws and the Uniform Code of Military Justice (UCMJ).
12.2 SPILL RESPONSE AND EMERGENCY PROCEDURES
Any person discovering a spill or release of oil or hazardous substances must immediately
report the incident to his/her supervisor. The supervisor will determine if the spill is minor
and should be cleaned up without further notification, or if further notification is required.
If a supervisor cannot be quickly notified or if a major spill threatens personnel safety or
may reach surface waters, storm drains, or sanitary sewer drains, the Fire and
Emergency Services Division (Directorate of Public Safety) must be notified immediately
by calling 911.
The employee or supervisor reporting a spill to the Fire and Emergency Services Division
should provide the following information to the fullest extent known:
1. Location, time, and type of incident (spill, fire, injury, etc.)
2. Name and quantity of spilled material, and the rate of release (an estimate is OK
if not known)
3. Provide a safety data sheet for spilled material if readily available; can be faxed to
the Fire and Emergency Services Division (if it can be done quickly) or provided at
the time of their arrival to the scene
4. Direction of the spill, vapor, or smoke release
5. Fire and/or explosion possibility
6. Coverage area of spill, and intensity of any fire or explosion (if applicable)
7. The extent of injuries (if any)
SECTION TWELVE Spill Response Procedures
12-2
As part of the existing notification procedures, the Fire and Emergency Services Division
will always notify DPW-ENRD so there is no need for the reporter of the spill to place a
second call to DPW-ENRD once the Fire and Emergency Services Division has been
notified.
When the Fire and Emergency Services Division has determined that there is no longer
a threat to life or property, DPW-ENRD will serve as the on-scene coordinator and will
determine if the spill is reportable to others as required by the ISCP. Cleanup assistance
and remediation of the site (if necessary) will be provided by the installation maintenance
support contractor. The organization responsible for the spill will be billed later for any
cleanup or remediation expenses.
The organization responsible for the spill or release must complete a written spill report
and email or fax it to DPW-ENRD at james.d.hager.civ@mail.mil or (334) 255-2058 within
five days of the incident (USAACE Form 2718, Spill Notification Form).
12.3 SPILL CONTINGENCY PLANS
The Fort Rucker SPCC Plan and ISCP are required reading for all personnel who manage
or supervise hazardous waste activities and for all organization emergency response
coordinators. Copies of both of these plans are available on the Sustainable Fort Rucker
website.
Each organization generating or storing hazardous waste shall prepare and possess a
hard copy of the organization’s Site Specific Spill Plan for waste handling and storage
areas using USAACE Form 2719, Site Specific Spill Plan. A copy of the form is located
in Appendix T. The plan shall be designed to minimize hazards to human health and the
environment from fires, explosions, and any unplanned releases of hazardous
constituents to the air, soil, or surface water. The provisions of the plan shall be carried
out whenever there is a fire, explosion, or release of hazardous waste or constituents
which could threaten human health or the environment.
All organization personnel who manage or handle hazardous wastes shall read and
understand all procedures contained in the Site Specific Spill Plan, and shall receive initial
training and annual update training in executing the procedures as they pertain to their
SECTION TWELVE Spill Response Procedures
12-3
positions. A copy of the Site Specific Spill Plan will be maintained at all organization waste
generation, management, and storage areas. The plan will be reviewed annually and
amended whenever:
a. The plan fails in an emergency.
b. The facility changes design, construction, operation, location, procedures, or other
circumstances that require changes in established emergency response
procedures.
c. The organization emergency coordinator and/or emergency equipment changes.
12.4 SPILL CONTINGENCY TRAINING
At least once per year, all organizations (including contractors) must provide initial or
update training for all employees who handle or use hazardous materials, hazardous
waste, and/or oil/fuel of any type in quantities equal to or greater than one quart at a time
(this requirement does not include refueling a ground vehicle at a fuel pump). New
employees must not be allowed to perform any operations involving hazardous materials,
hazardous waste, or oil/fuel without direct supervision until they receive training. Training
will, at a minimum, cover the following subjects:
• ISCP requirements
• General requirements of the SPCC Plan
• Container-specific requirements of the SPCC Plan applicable to their assignments
12.5 SPILL CONTINGENCY SUPPLIES
All organizations must maintain adequate stocks of spill control supplies and equipment
to handle spills. Spill contingency supplies are available at the HMCC and through
commercial catalogs. These supplies include dry sweep and absorbent pads and booms
at a minimum. Organizations should use absorbents that are part of the continued use
program whenever possible. Additional details about requirements for spill contingency
supplies are included in the ISCP.
12.6 SPILL REPORTING
In addition to the reporting that is required for implementation of the contingency plan,
spills of hazardous waste that exceed the reportable quantity must be reported to
SECTION TWELVE Spill Response Procedures
12-4
appropriate agencies, including the National Response Center (NRC), EPA, and ADEM.
The ISCP and the SPCC Plan discuss the details of the required notifications when a
release occurs. DPW-ENRD is responsible for reporting to the State in the event of a spill.
The Fort Rucker Fire Department is responsible for any reporting to the NRC. Any reports
to these agencies must be coordinated through DPW-ENRD.
Appendix A Waste Disposal Data CY10-CY15
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REGULATED WASTE CY10 CY11 CY12 CY13 CY14 CY15Absorbent Materials - Contaminated with Cadmium, Chromium, and/or Lead 36,402 22,388 19,368 18,206 14,193 10,531
Absorbent Materials/Filters - Contaminated with Paint 28,340 16,926 18,838 16,730 17,361 10,242
Paint and Thinner 15,305 11,892 8,375 8,797 7,932 6,020Abrasive Blast Media 11,245 4,760 5,125 9,420 8,940 3,364Clarus Parts Washer Liquid 10,477 6,738 7,532 4,621 6,339 4,591Petroleum Lab Waste (Heptane/Toluene) 5,569 4,966 6,854 5,065 3,755 3,925Other Paint and Related Materials 0 0 0 0 0 1,796Acids 410 377 71 13 21 72Clarus Parts Washer Filters 86 148 258 233 484 245Fixer/Developer 4,820 660 0 0 0 0Caustic Cleaning Compounds 0 0 2,605 284 227 27Plating Shop Solids 1,235 1,844 3,580 2,350 2,610 730Expired Adhesives 257 373 382 0 71 133Expired Corrosive Chemicals 0 609 0 0 0 47Crushed/Broken Bulbs 16 470 5 491 326 349Carbon Remover 829 0 0 0 0 750Chemical Defense Equipment (CDE) 0 0 509 392 71 0Alodine Waste 177 0 0 0 0 150Expired Military Equipment 0 1,005 0 0 0 191Oxidizing Materials 0 23 0 0 0 36Aerosols 332 103 87 80 167 245Lead Based Paint and Debris 0 0 10,888 673 0 94Other Waste from Aircraft Maintenance 297 2,607 926 0 0 617Denatured Alcohol (noncompliant) 703 0 0 56 61 0Medical Waste 146 99 154 0 0 378TOTAL (LBS) 116,646 75,988 85,557 67,411 62,558 45,636*TOTAL (TONS) 58 38 43 34 31 23*Includes 1,103 lbs. one-time waste
UNIVERSAL WASTE CY10 CY11 CY12 CY13 CY14 CY15Batteries (Ni-Cad and Lithium) 2,033 801 1,066 1,088 9,036 1,122Fluorescent Lamps 8,538 7,541 6,125 5,915 6,976 6,726TOTAL (LBS) 10,571 8,342 7,191 7,003 16,012 7,848TOTAL (TONS) 5 4 4 4 8 4
Waste Disposal Data
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Appendix B USAACE Form 2735, Hazardous Waste Job Description and Training
Record
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HAZARDOUS WASTE MANAGEMENT JOB DESCRIPTION AND TRAINING RECORD For use of this form, see the Hazardous Waste Management Plan; the proponent is DPW-ENRD
USAACE FORM 2735, rev 23MAY11 Page 1 of 3 THIS IS A CONTROLLED DOCUMENT. REPLACES EMS-F035, WHICH IS OBSOLETE VERIFY MOST RECENT VERSION ONLINE.
Under penalty of federal and state laws, job descriptions and training documentation relating to hazardous waste management must be kept on file for all personnel on Fort Rucker that collect, process, treat, dispose, recover, transport, or store hazardous waste. The following form is provided to assist in compliance with the above stated laws. Location of filing for this form is at the discretion of the commander/ supervisor but must be available for inspections by the Alabama Department of Environmental Management (ADEM), Environmental Protection Agency (EPA), and DPW-ENRD.
NAME
ORGANIZATION JOB TITLE JOB DESCRIPTION (As related to hazardous waste management only) Personnel job position relating to hazardous waste management includes: Handling/disposing/storing/ transporting hazardous waste generated by one or more of the following: (check applicable portions below):
Aviation Maintenance
Motorpool Maintenance
Adhesives, Sealants and Paints
Arms Room
Use of Cleaning Solvents
Medical/Dental Operations
Photographic Developing Laboratories or Printing Facilities
Laboratory Operations
Batteries (including Lithium, Magnesium, Mercury, Nickel-Cadmium, & Lead Acid)
Pesticides, Insecticides, Rodenticides, Herbicides, Fungicides
Nuclear, Biological, and Chemical (NBC) Material
Other:
DUTIES (As related to hazardous waste management only) DATE ASSUMED DUTIES: The above person’s duties have a direct effect on hazardous waste management and/or hazardous waste accumulation, whether by direct contact with the hazardous waste or through hazardous waste management activities, must receive training. This individual has the appropriate qualifications to read, understand, apply, and communicate written and verbal information regarding handling and managing hazardous wastes. Responsibilities include:
90-Day HWAS Manager HWSAP Manager Environmental Officer EPOC HW Handling
Placing HW in HWSAP Documenting HW Activities Receiving HW
Transporting HW
Inspecting HWSAP
Inspecting 90-Day HWAS
Emergency Response
TRAINING (As related to hazardous waste management only) Personnel must receive hazardous waste management training within six months of assumption of duties involving hazardous waste. Personnel may not perform hazardous waste management duties unsupervised until completion of training. The training program must be directed by a person trained in hazardous waste management procedures, and must include instruction which teaches facility personnel hazardous waste management procedures (including contingency plan implementation) relevant to the positions in which they are employed. All personnel trained must complete an annual review of the initial training. At a minimum, the training program must be designed to ensure that facility personnel are able to respond effectively to emergencies by familiarizing them with emergency procedures, emergency equipment, and emergency systems, including where applicable:
1. Procedures for using, inspecting, repairing, and replacing facility emergency and monitoring equipment; 2. Key parameters for automatic waste feed cut-off systems; 3. Communications or alarm systems; 4. Response to fires or explosions; 5. Response to groundwater contamination incidents; and 6. Shutdown of operations.
HAZARDOUS WASTE MANAGEMENT JOB DESCRIPTION AND TRAINING RECORD For use of this form, see the Hazardous Waste Management Plan; the proponent is DPW-ENRD
USAACE FORM 2735, rev 23MAY11 Page 2 of 3 THIS IS A CONTROLLED DOCUMENT. REPLACES EMS-F035, WHICH IS OBSOLETE VERIFY MOST RECENT VERSION ONLINE.
NAME Defense Hazardous Materials/ Hazardous Waste Handling Class – Provided by: ALMC
Initial Training (24 hrs) Date:
Annual Refresher Training (8 hrs) Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
On-the-Job Training – Provided by: Initial Training Date:
Annual Refresher Training Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date: Hazardous Waste Satellite Accumulation Point Manager Training – Provided by: DPW-ENRD Initial Training (2 hrs) Date:
Annual Refresher Training (2 hrs) Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
HAZARDOUS WASTE MANAGEMENT JOB DESCRIPTION AND TRAINING RECORD For use of this form, see the Hazardous Waste Management Plan; the proponent is DPW-ENRD
USAACE FORM 2735, rev 23MAY11 Page 3 of 3 THIS IS A CONTROLLED DOCUMENT. REPLACES EMS-F035, WHICH IS OBSOLETE VERIFY MOST RECENT VERSION ONLINE.
NAME 90-Day Hazardous Waste Accumulation Site Manager Training – Provided by: DPW-ENRD Initial Training (2 hrs) Date:
Annual Refresher Training (2 hrs) Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date: Environmental Officer Training – Provided by: DPW-ENRD
Initial Training (16 hrs) Date:
Annual Refresher Training (4 hrs) Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date: Environmental Point of Contact (EPOC) Training – Provided by: DPW-ENRD
Initial Training (4 hrs) Date:
Annual Refresher Training (4hrs) Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
Date: Date: Date:
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Appendix C USAACE Form 2729, EO/EPOC Appointment Memo
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ENVIRONMENTAL OFFICER / ENVIRONMENTAL POINT OF CONTACT APPOINTMENT MEMO
For use of this form, see GC Policy Memo 13-35; the proponent is DPW-ENRD
USAACE FORM 2729, rev 28FEB13 Page 1 of 2 THIS IS A CONTROLLED DOCUMENT. PREVIOUS EDITIONS ARE OBSOLETE VERIFY MOST RECENT VERSION ONLINE.
(office symbol)
(date)
MEMORANDUM FOR SEE DISTRIBUTION SUBJECT: Environmental Officer or Environmental Point of Contact (EPOC) Appointment 1. The individuals listed in the attached table are appointed as the Environmental Officer or EPOC for their assigned work areas. 2. Authority for this appointment is Army Regulation 200-1, paragraphs 1-27.a.(15) and 1-32.f., which require installation and tenant commanders/directors to appoint and train Environmental Officers at appropriate organizational levels to ensure required environmental actions are taking place. Appropriate levels of appointment are discussed in the Environmental Officer and EPOC Appointment and Training Plan. 3. Purpose: To perform duties as Environmental Officer or EPOC. 4. Period: Until reassigned or relieved of these duties. 5. Special Instructions: Appointees must attend the Environmental Officer or EPOC Course (as appropriate to duties) within six months after being appointed and attend an annual refresher thereafter. POC NAME: PHONE:
COMMENTS:
(signature block)(signature block)(signature block)
DISTRIBUTION: ORGANIZATION COMMANDER/DIRECTOR CURRENT ENVIRONMENTAL OFFICER/EPOC NEWLY APPOINTED INDIVIDUAL DPW-ENRD (ATTN Ms. Melissa Lowlavar, melissa.lowlavar3.civ@mail.mil)
ENVIRONMENTAL OFFICER / ENVIRONMENTAL POINT OF CONTACT APPOINTMENT MEMO
For use of this form, see GC Policy Memo 13-35; the proponent is DPW-ENRD
USAACE FORM 2729, rev 28FEB13 Page 2 of 2 THIS IS A CONTROLLED DOCUMENT. PREVIOUS EDITIONS ARE OBSOLETE VERIFY MOST RECENT VERSION ONLINE.
NAME EO or EPOC EMAIL LOCATION
*NOTE: Organizations may substitute an organization-generated table containing at least the information specified in this template. Attach additional pages as necessary.
Appendix D USAACE Form 2733, HWSAP and 90-Day HWAS Manager
Appointment Memo
HAZARDOUS WASTE SATELLITE ACCUMULATION POINT (HWSAP) OR 90-DAY HAZARDOUS
WASTE ACCUMULATION SITE (90-HWAS) MANAGER APPOINTMENT MEMO For use of this form, see the Hazardous Waste Management Plan; the proponent is DPW-ENRD
USAACE FORM 2733, rev 28SEP12 Page 1 THIS IS A CONTROLLED DOCUMENT. PREVIOUS EDITIONS ARE OBSOLETE VERIFY MOST RECENT VERSION ONLINE.
(office symbol)
(date)
MEMORANDUM FOR SEE DISTRIBUTION SUBJECT: HWSAP or 90-HWAS Manager Appointment 1. The individuals listed in the attached table are appointed as the HWSAP or 90-HWAS Managers for their assigned work areas. 2. Authority for this appointment is the Hazardous Waste Management Plan (HWMP) Section 3, which requires appointment of a HWSAP and 90-HWAS manager for each HWSAP and 90-HWAS location on Fort Rucker. The requirement to have a HWMP is included in AR 200-1 Section 10-1d(3). 3. Purpose: To perform duties as HWSAP or 90-HWAS Manager as specified in the HWMP. 4. Period: Until reassigned or relieved of these duties. 5. Special Instructions: Appointees must attend the HWSAP Manager or 90-HWAS Manager Course (as appropriate to duties) within six months after being appointed and attend an annual refresher thereafter.
POC NAME: PHONE: COMMENTS:
(signature block)
(signature block)
DISTRIBUTION: ORGANIZATION COMMANDER/DIRECTOR CURRENT MANAGER NEWLY APPOINTED INDIVIDUAL DPW-ENRD (ATTN Ms. Colleen Quinlan, colleen.quinlan3@us.army.mil)
USAACE FORM 2733, rev 28SEP12 Attachment 1 THIS IS A CONTROLLED DOCUMENT. PREVIOUS EDITIONS ARE OBSOLETE VERIFY MOST RECENT VERSION ONLINE.
Name HWSAP or 90-HWAS
Primary or Alternate Phone Location Person Replaced
*NOTE: Organizations may substitute an organization-generated table containing at least the information specified in this template. Attach additional pages as necessary. Indicate N/A in the line for person replaced if the individual is not replacing someone else with this appointment.
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Appendix E Inspection Forms
USAACE Form 2725, HWSAP Inspection Checklist USAACE Form 2726, 90-HWAS Inspection Log
USAACE Form 2711, SPCC Plan Container Inspection Form
USAACE Form 2717, Environmental Compliance Inspection Checklist
This page left intentionally blank.
SPILL PREVENTION, CONTROL, AND COUNTERMEASURES PLAN CONTAINER INSPECTION CHECKLISTFor use of this form, see the SPCC Plan; the proponent is DPW-ENRD
Inspector:
Number of Containers:
Date of Inspection:CONTAINER
YES NO N/A YES NO N/A YES NO N/A YES NO N/A YES NO N/A
SECONDARY CONTAINMENT
Secondary Containment Type:
YES NO N/A YES NO N/A YES NO N/A YES NO N/A YES NO N/A
COMMENTS
Organization:
Choose the Container ID from the pull down list.
Container Type:
Location:
CONTAINER IDCONTAINER ID CONTAINER ID CONTAINER ID CONTAINER ID
Is coating in good condition?
Are gauges present and functioning properly for main container?
Are gauges present and functioning properly for interstitial space of double-walled container?
Is container in good condition (no holes, rust, dents, leaks, etc.)?
Is piping in good condition (no holes, rust, dents, leaks, etc.)?
Is container clearly labeled as to content?
Is capacity of the container clearly labeled?
Have spills been cleaned (i.e., no visible oil/product near container, on container surface, or in secondary containment)?
Are valves, fill ports, lids and any other openings sealed/closed when not in use?
Material Stored:
Container Purpose:
Are emergency release valves present and operational?
Turn in completed forms to Melissa Lowlavar in bldg 1121 or email to melissa.g.lowlavar3.civ@mail.mil
NOTE: Structrual containment includes buildings, dikes, berms, etc. If no secondary containment is present, notify DPW-ENRD.
If rainwater collects in secondary containment, is it inspected for contamination and properly discharged at least weekly?
Is secondary containment valve kept closed?
Is secondary containment sufficiently impervious to contain spills/leaks (i.e., no cracks, visible vegetation, etc.)?
Are spill response supplies (i.e., absorbents, spill kits) available in sufficient quantities?
Note: Any deficiencies should be corrected immediately if possible (i.e., spills, open containers, etc.). Items requiring a work order for repair should be identified in this section with work order numbers.
Is secondary containment checked and found to be free of material?
Double-walled
Structural None
Double-walled
Structural None
Double-walled
Structural None
Double-walled
Structural None
Double-walled
Structural None
USAACE FORM 2711 (rev 31MAR15) PREVIOUS EDITION IS OBSOLETE
THIS IS A CONTROLLED DOCUMENT. VERIFY THE LATEST VERSION ONLINE.
SPILL PREVENTION, CONTROL, AND COUNTERMEASURES PLAN CONTAINER INSPECTION CHECKLISTFor use of this form, see the SPCC Plan; the proponent is DPW-ENRD
Container Type:
Container Purpose:
Inspection Date:CONTAINER
YES NO N/A YES NO N/A YES NO N/A YES NO N/A YES NO N/A YES NO N/A
SECONDARY CONTAINMENTSecondary Containment Type:
YES NO N/A YES NO N/A YES NO N/A YES NO N/A YES NO N/A YES NO N/A
Is secondary containment checked and found to be free of material?
COMMENTS
Organization:
Turn in completed forms to Melissa Lowlavar in bldg 1121 or email to melissa.g.lowlavar3.civ@mail.mil
NOTE: Structrual containment includes buildings, dikes, berms, etc. If no secondary containment is present, notify DPW-ENRD.
If rainwater collects in secondary containment, is it inspected for contamination and properly discharged at least weekly?
Is secondary containment valve kept closed?
Is secondary containment sufficiently impervious to contain spills/leaks (i.e., no cracks, visible vegetation, etc.)?
Are spill response supplies (i.e., absorbents, spill kits) available in sufficient quantities?
Note: Any deficiencies should be corrected immediately if possible (i.e., spills, open containers, etc.). Any items that require a work order for repair should be identified in this comment section with applicable work order numbers.
Have spills been cleaned (i.e., no visible oil/product near the container, on the container surface, or in secondary containment)?
Are valves, fill ports, lids and any other openings sealed/closed when not in use?
Are gauges present and functioning properly for main container?
Are gauges present and functioning properly for interstitial space of double-walled container?
Are emergency release valves present and operational?
Is container in good condition (no holes, rust, dents, leaks, etc.)?
Is piping in good condition (no holes, rust, dents, leaks, etc.)?
Is container clearly labeled as to content?
Is capacity of the container clearly labeled?
Is coating in good condition?
CONTAINER ID CONTAINER ID CONTAINER ID CONTAINER ID CONTAINER ID CONTAINER ID
DPW ID DPW IDInspector:
Choose the DPW ID from the pull down list. DPW ID DPW ID DPW ID DPW ID
AST Belly Tank
Fire PumpGEN
Double-walled
Structural None
Double-walled
Structural None
Double-walled
Structural None
Double-walled
Structural None
Double-walled
Structural None
Double-walled
Structural None
AST Belly Tank
Fire PumpGEN
AST Belly Tank
Fire PumpGEN
AST Belly Tank
Fire PumpGEN
AST Belly Tank
Fire PumpGEN
AST Belly Tank
Fire PumpGEN
USAACE FORM 2711 (rev 31MAR15) PREVIOUS EDITION IS OBSOLETE
THIS IS A CONTROLLED DOCUMENT. VERIFY THE LATEST VERSION ONLINE.
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HAZARDOUS WASTE SATELLITE ACCUMULATION POINT INSPECTION CHECKLISTFor use of this form, see the Hazardous Waste Management Plan; the proponent is DPW-ENRD
Date: Date: Date: Date: Date:Initials: Initials: Initials: Initials: Initials:
1)2)3)4)
5)
6)7)
1)
2)
1)2)3)
4)
5)6)
7)
1)
2)
MONTH:
NOTES (unsatisfactory observations, explanations and corrections to be noted with date and corrective actions taken.)
Employee training records are maintained, readily accessible, and documented on USAACE Form 2735
Facility personnel are trained in HW handling and emergency response
C. PREPAREDNESS & PREVENTION
Spill control equipment is availableFire control equipment is availableCommunication equipment is available and working
B. ACCUMULATION TIME
√ -- If satisfactory U – If unsatisfactory
A. CONTAINER MANAGEMENT
HW is under the control of the generatorHW is collected at or near the point of generation
Aisles are clear for emergency evacuationThe equipment listed above is maintained
Decontamination equipment (e.g. shower, eye wash) is available
D. PERSONNEL TRAINING
A Site Specific Spill Plan and ISCP exists for facility and signage indicates emergency contact
WEEK 5WEEK 2 WEEK 3 WEEK 4LOCATION:
Containers are closed
Full containers dated less than three days old
55-gallons or less of each HW stream is stored in the designated area (or 1-quart of “P” listed waste)
INSPECTOR (Alt):PHONE NO:INSPECTOR: WEEK 1
All HW containers are properly marked “Hazardous Waste” with contents and waste code(s)
Incompatible wastes are segregated
Wastes are in compatible containersContainers are in good condition (no damage or leaks)
USAACE FORM 2725 (rev 17DEC13)PREVIOUS EDITIONS ARE OBSOLETE
THIS IS A CONTROLLED DOCUMENT.VERIFY MOST RECENT VERSION ONLINE.
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90-DAY HAZARDOUS WASTE ACCUMULATION SITE (90-HWAS) INSPECTION LOGFor use of this form, see the Hazardous Waste Management Plan; the proponent is DPW-ENRD
DATE: 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31
TIME:
Site-Specific Spill Plan and ISCP readily available
Containers are less than 60 days old
HW accumulation start dates are noted
Containers are properly labeled (including EPA ID #)
Incompatible wastes are separated
Month Building FORT RUCKERYear
No evidence of leaks or spills
Containment Area - no holes or cracks
Wastes are compatible with containers
Containers are closed and free from leaks, rust or dents
INSPECTOR'S NAME(S) √ -- If Satisfactory U – If Unsatisfactory
HW storage area is secured to prevent unauthorized entry
INSPECTOR (INITIALS):
Number/capacity of containers noted
Adequate aisle space
Warning signs posted
Communication system (e.g. phone, alarm) active
Portable fire extinguisher on hand
Spill control equipment on hand
Training records complete and available
SPCC Plan readily available
Annotate corrective action(s) taken and date:
Note unsatisfactory observations and explain:
USAACE FORM 2726 (rev 23 MAY11)REPLACES EMS-F026, WHICH IS OBSOLETE
THIS IS A CONTROLLED DOCUMENT.VERIFY MOST RECENT VERSION ONLINE.
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Appendix F ADEM Letters and Guidance
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Alabama Department of Environmental Management Land Division P. O. Box 301463 Montgomery, AL 36130-1463 Telephone 334-271-7730 Fax 334-279-3050
January 2014
Hazardous Waste Management
Management of Aerosol Containers
Information presented in this fact sheet is intended to provide a general understanding of the regulatory requirements governing the management of disposable aerosol containers. This information
is not intended to replace, limit, or expand upon the complete regulatory requirements found in Division 14 of the Alabama Department of Environmental Management Administrative Code.
WHAT IS AN AEROSOL CONTAINER?
An aerosol container is a dispenser that holds a substance under pressure and that can release the substance,
usually by means of a propellant gas, in a number of forms such as wet sprays, fine sprays, powder sprays, foams,
or pastes. Common liquefied propellants include propane, butane, and isobutane.
WHAT ARE THE SAFETY AND ENVIRONMENTAL CONCERNS FOR AEROSOL CONTAINERS?
Some aerosol products (for example, paints, solvents, and pesticides) are hazardous due to the presence of
hazardous ingredients. Aerosol products should be used with adequate ventilation and/or personal protective
equipment to prevent inhalation and exposure that may result in harmful health effects. Extreme temperatures may
cause containers to rupture and moisture may cause them to rust, resulting in a release of the contents to the
environment. Many aerosol containers pose a fire hazard because they contain highly flammable propellants such
as propane and butane. Pressurized containers present additional concerns. If punctured, the contents may be
released so forcefully that injuries can result. Also, pressurized containers delivered to a landfill present safety
concerns during compacting.
Spent Aerosol Can Management
I will RECYCLE my cans.
Are the cans empty?
Yes:
Empty aerosol cans being
recycled are excluded from
management as solid (and
therefore hazardous) waste.
[See 335-14-2-.01(4)(a)13.]
No:
Cans may be recycled, but the
contents are solid wastes
subject to a hazardous waste
determination. Any liquids or
propellants removed from the
cans must be managed in
accordance with ADEM div.
14 requirements.
[See 335-14-2-.01(6)(a)3.(ii)
and 335-14-3-.01(2)]
How will you manage your spent
aerosol cans?
I will DISPOSE my cans.
Are the cans empty?
Yes:
Aerosol cans that are empty and
fully depressurized may be
disposed of as solid waste,
which are subject to a hazardous
waste determination.
[See 335-14-2-.01(7) and
335-14-3-.01(2)]
No:
A discarded aerosol can is a
hazardous waste if the can and
its contents exhibit a hazardous
waste characteristic or if it is a
listed hazardous waste.
[See 335-14-3-.01(2)]
“Empty” means the aerosol can does not contain a significant amount of free liquid and also that the propellant
has been used up so that the pressure in the can is at or near atmospheric pressure. This can usually be determined
during the normal use of the product in the manner it was intended to be used. If you cannot demonstrate that the
can is empty then it must be emptied by the means ordinarily used to render aerosol cans empty (e.g. the can must
be punctured, crushed, or shredded and in the process the gas and the liquid must be contained/captured and
Disposable Aerosol Containers
Page 2 of 3
managed appropriately). If your aerosol can held an acute hazardous waste it must be triple rinsed to be
considered “empty”. [See 335-14-2-.01(7)]
WHAT IS THE PREFERRED MANAGEMENT METHOD FOR AEROSOL CONTAINERS?
•••• Empty the container, either through normal use or by puncturing and draining.
•••• When puncturing a container, collect both the liquid and the gas in an appropriate collection device.
•••• Send the empty container to a scrap metal recycler.
•••• Dispose of the collected residues appropriately, based on their regulatory status - either as solid or
hazardous waste.
While landfill disposal of the empty containers is an acceptable alternative, it is the least preferred option.
MAY I USE A DEVICE TO PUNCTURE AEROSOL CONTAINERS?
Companies that regularly generate significant numbers of waste aerosol containers may be interested in using a
device to puncture and drain the containers. Punctured, drained aerosol containers are known as “processed scrap
metal”, which is exempt from the solid waste regulations so long as it is recycled. Use of such a device does not
require a waste-treatment permit at this time. If you choose to use one, consider the following precautions:
• Do not puncture containers with any of these ingredients: ethyl ether (often in starting fluids), chlorinated
compounds, pesticides, freons and foamers, oven cleaners, unknowns. These should be lab-packed and
managed as hazardous waste.
• Follow the manufacturer’s instructions for operating, cleaning, and maintaining the device.
• Employees operating the device should be thoroughly trained in its use and should wear appropriate
personal protective equipment.
• Sort containers by size and puncture similar sizes at the same time. You may wish to puncture containers
with solvents, degreasers, and/or lubricants last to help clean the device.
• Operate only in an open, well-ventilated area. Avoid confined spaces.
• Collect liquids in an appropriate hazardous waste container.
• Keep the unit closed when it is not in use.
• Puncturing spent aerosol cans for recycling is considered a form of treatment under ADEM Admin. Code r.
335-14-8-.01(1)(c)2.(x). According to that rule, you do not need a permit, but you must notify the
Department at least 60 days in writing before you begin puncturing cans.
HOW SHOULD I MANAGE AEROSOL CONTAINERS THAN CANNOT BE EMPTIED?
•••• First try to return or exchange malfunctioning aerosol containers. Malfunctioning aerosol containers
returned to the supplier or manufacturer are considered “products”, not “wastes”.
•••• Non-empty aerosol containers that cannot be returned or exchanged must usually be managed as a
hazardous waste, depending on the specific contents (including propellants, which are often flammable).
HOW CAN I REDUCE MY AEROSOL CONTAINER WASTE?
� Determine whether or not a product is needed. Could the process using the aerosol be eliminated?
� Could a non-aerosol product be used instead of the aerosol product?
� If required, choose a non-hazardous product, or the least hazardous product, that will do the job.
� Use only as much as is needed.
� Store aerosol containers away from moisture, sunlight, and extreme heat or cold.
� Follow the label instructions to clean the nozzle after each use.
� Use the entire contents of a container before buying more.
� Purchase according to demand so that the product’s shelf life does not expire.
� Consider purchasing products in bulk and using either a refillable container with compressed air as the
propellant or a non-aerosol pump applicator.
Disposable Aerosol Containers
Page 3 of 3
WHERE CAN I GET ADDITIONAL INFORMATION?
ADEM Administrative Code rules (ADEM Admin. Code rs)
provide more in-depth information regarding the status of metal that will be recycled.
335-14-2-.01(7) provides a full definition of “RCRA Empty containers”, while “processed scrap metal” is defined
at ADEM Admin. Code r. 335-14-1-.02(1)(a)208.
On-Line Resources
Earth 911 - http://earth911.com
ADEM Home Page - http://www.adem.alabama.gov
ADEM Administrative Code Division 14
ADEM Guidance - http://www.adem.alabama.gov/programs/land/guidanceReports.cnt
Hazardous Waste Determination
Hazardous Waste: The Basics
Notification of Regulated Waste Activity
ADEM Publications - http://www.adem.alabama.gov/MoreInfo/publications.cnt
RCRA Small Quantity Generator Handbook
US Environmental Protection Agency’s Homepage
Telephone Resources
ADEM Ombudsman
Hazardous Waste Compliance Inspectors
*Adapted from the following sources: Oregon Department of Environmental Quality Program Implementation Guidance Number 2005
Nebraska Department of Environmental Quality Environmental Guidance
WHERE CAN I GET ADDITIONAL INFORMATION?
(ADEM Admin. Code rs) 335-14-2-.01(4)(a)13. and 335
depth information regarding the status of metal that will be recycled. ADEM Admin. Code r.
.01(7) provides a full definition of “RCRA Empty containers”, while “processed scrap metal” is defined
.02(1)(a)208.
http://www.adem.alabama.gov
ADEM Administrative Code Division 14 - http://www.adem.state.al.us/alEnviroRegLaws/files/Division14.pdf
http://www.adem.alabama.gov/programs/land/guidanceReports.cnt
Notification of Regulated Waste Activity
http://www.adem.alabama.gov/MoreInfo/publications.cnt :
Quantity Generator Handbook
US Environmental Protection Agency’s Homepage - http://www.epa.gov
Telephone Resources
ADEM Ombudsman - - - - - - - - - - - - - - - - - - - 800-533- 2336
Hazardous Waste Compliance Inspectors - - - 334-271-7730
*Adapted from the following sources: Oregon Department of Environmental Quality Program Implementation Guidance Number 2005
Nebraska Department of Environmental Quality Environmental Guidance Document 03-067, dated December 2003.
.01(4)(a)13. and 335-14-2-.01(6)(a)3.(ii)
ADEM Admin. Code r.
.01(7) provides a full definition of “RCRA Empty containers”, while “processed scrap metal” is defined
http://www.adem.state.al.us/alEnviroRegLaws/files/Division14.pdf
2336
7730
*Adapted from the following sources: Oregon Department of Environmental Quality Program Implementation Guidance Number 2005-PO-001 (dated 07/24/2005);
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Appendix G USAACE Form 2716, Secondary Containment Drainage Activity Log
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Location
DATE START TIME END TIME
FREE OF SHEEN OR OTHER
MATERIAL/ WASTE?*
NAME
SECONDARY CONTAINMENT DRAINING ACTIVITY LOG
For use of this form, see the Spill Prevention, Control, and Countermeasures (SPCC) Plan; the proponent is DPW-ENRD
*NOTE: If a sheen is present, contact the Environmental Office at 255-1657 for further information.
NEVER DISCHARGE ANY WATER WITH A SHEEN OR EVIDENCE OF ANY HAZARDOUS MATERIAL OR
HAZARDOUS WASTE. THE DISCHARGE OF WATER WITH A SHEEN OR OTHER CONTAMINATION MAY LEAD
TO A VIOLATION OF THE FORT RUCKER STORMWATER DISCHARGE PERMIT.
USAACE FORM 2716 (rev 31MAR15) PREVIOUS EDITION IS OBSOLETE
THIS IS A CONTROLLED DOCUMENT.VERIFY THE LATEST VERSION ONLINE.
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Appendix H DD Form 1348-1A, Issue Release/Receipt Document
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2 3 4 5 6 7 2 2 2 2 2 2 2 4 4 4 4 4 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 7 7 7 7 7 7 7 7 7 7
8 1. TOTAL PRICE 2. SHIP FROM 3. SHIP TO
3 4 5 6 7 8 9 5 6 7 8 9 0 1 2 3 4 5 6 7 8 9 0 1 2 3 4 5 6 7 8 9 0 1 2 3 4 5 6 7 8 9 0
RI M U I QUANTITY SUPPLE- S F DIS- PR0- P R D D A RI O C M UNIT PRICE D OLLARS CTS
FROM & N S S MENTARY I U TRI- JECT R E E A D / O G
S I S E ADDRESS G N BU- I Q L T V P N T DOLLA RS CTS
T R D TION D E D $
$ 4. MARK FOR
24. DOCUMENT NUMBER & SUFFIX (30-44) 5. DOC DATE 6. NMFC 7. FRT RATE 8. TYPE CARGO 9. PS
DOC:
DOT SHIPPING NAME:
10. QTY. REC’D 11. UP 12. UNIT WEIGHT 13. UNIT CUBE 14. UFC 15. SL
25. NATIONAL STOCK NO & ADD (8-22) NSN:
lbs
16. FREIGHT : See below
BILL TO: 17. ITEM
LOCATION: 18. TY CONT 19. NO CONT 20. TOTAL
WEIGHT 21. TOTAL CUBE
1 LBS 22. RECEIVED BY 23. DATE RECEIVED 26. RIC(4-6), UI(23-24), QTY(25-29), CON CODE(71), COG(55-56), UP(74-80) Return Part 2 to:
27. ADDITIONAL DATA POC: WASTE CODES:
CLIN: DISPOSAL COST: $
TOTAL COST: $
The above name materials are properly classified, described, packaged, marked, and labeled and are in proper condition for transportation according to the applicable regulations of the Department of Transportation (49 CFR 170-189)
PROFILE NUMBER: CERTIFIED BY:(SIGN) (PRINT)
ASD: EPA ID:
INSPECTED BY: (SIGN) (PRINT) DD FORM 1348-1A, JAN 96 ISSUE RELEASE/RECEIPT DOCUMENT FORM APPROVED, OMB NO 0704-0188
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Appendix I 49 CFR 172.400 Excerpt
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399
Pipeline and Haz. Matls. Safety Admin., DOT § 172.400
Packaging: When: Then the alter-native marking re-quirement is:
On one end of nurse tanks if that end con-tains valves, fit-tings, regulators or gauges when those appur-tenances pre-vent the mark-ings and placard from being prop-erly placed and visible.
They meet the provisions of § 173.315(m) of this subchapter.
N/A.
On cargo tanks, in-cluding compart-mented cargo tanks, or tank cars.
They contain more than one petro-leum distillate fuel.
The identification number for the liquid petroleum distillate fuel having the low-est flash point is displayed. If the cargo tank also contains gaso-line and alcohol fuel blends con-sisting of more than 10% eth-anol the identi-fication number ‘‘3475’’ or ‘‘1987,’’ as ap-propriate, must also be dis-played.
(d) When a bulk packaging is labeled
instead of placarded in accordance with
§ 172.514(c) of this subchapter, identi-
fication number markings may be dis-
played on the package in accordance
with the marking requirements of
§ 172.301(a)(1) of this subchapter.
[Amdt. 172–101, 45 FR 74667, Nov. 10, 1980, as
amended by Amdt. 172–74, 47 FR 40365, Sept.
30, 1982; Amdt. 172–109, 52 FR 13038, Apr. 20,
1987; Amdt. 172–110, 52 FR 29528, Aug. 10, 1987;
Amdt. 172–123, 55 FR 52593, Dec. 21, 1990; 56
FR 66255, Dec. 20, 1991; 65 FR 50459, Aug. 18,
2000; 73 FR 4716, Jan. 28, 2008; 76 FR 43527,
July 20, 2011; 78 FR 14714, Mar. 7, 2013; 78 FR
65478, Oct. 31, 2013]
§ 172.338 Replacement of identification numbers.
If more than one of the identification
number markings on placards, orange
panels, or white square-on-point dis-
play configurations that are required
to be displayed are lost, damaged or de-
stroyed during transportation, the car-
rier shall replace all the missing or
damaged identification numbers as
soon as practicable. However, in such a
case, the numbers may be entered by
hand on the appropriate placard, or-
ange panel or white square-on-point
display configuration providing the
correct identification numbers are en-
tered legibly using an indelible mark-
ing material. When entered by hand,
the identification numbers must be lo-
cated in the white display area speci-
fied in § 172.332. This section does not
preclude required compliance with the
placarding requirements of subpart F
of this subchapter.
[Amdt. 172–110, 52 FR 29528, Aug. 10, 1987]
Subpart E—Labeling
§ 172.400 General labeling require-ments.
(a) Except as specified in § 172.400a,
each person who offers for transpor-
tation or transports a hazardous mate-
rial in any of the following packages or
containment devices, shall label the
package or containment device with la-
bels specified for the material in the
§ 172.101 table and in this subpart:
(1) A non-bulk package;
(2) A bulk packaging, other than a
cargo tank, portable tank, or tank car,
with a volumetric capacity of less than
18 m3 (640 cubic feet), unless placarded
in accordance with subpart F of this
part;
(3) A portable tank of less than 3785 L
(1000 gallons) capacity, unless plac-
arded in accordance with subpart F of
this part;
(4) A DOT Specification 106 or 110
multi-unit tank car tank, unless plac-
arded in accordance with subpart F of
this part; and
(5) An overpack, freight container or
unit load device, of less than 18 m3 (640
cubic feet), which contains a package
for which labels are required, unless
placarded or marked in accordance
with § 172.512 of this part.
(b) Labeling is required for a haz-
ardous material which meets one or
more hazard class definitions, in ac-
cordance with column 6 of the § 172.101
table and the following table:
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49 CFR Ch. I (10–1–15 Edition) § 172.400a
Hazard class or division Label name
Label de-sign or sec-
tion ref-erence
1.1 .................................................................................... EXPLOSIVES 1.1 ............................................................ 172.411 1.2 .................................................................................... EXPLOSIVES 1.2 ............................................................ 172.411 1.3 .................................................................................... EXPLOSIVES 1.3 ............................................................ 172.411 1.4 .................................................................................... EXPLOSIVES 1.4 ............................................................ 172.411 1.5 .................................................................................... EXPLOSIVES 1.5 ............................................................ 172.411 1.6 .................................................................................... EXPLOSIVES 1.6 ............................................................ 172.411 2.1 .................................................................................... FLAMMABLE GAS .......................................................... 172.417 2.2 .................................................................................... NONFLAMMABLE GAS .................................................. 172.415 2.3 .................................................................................... POISON GAS .................................................................. 172.416 3 Flammable Liquid (Combustible liquid) ........................ FLAMMABLE LIQUID (none) .......................................... 172.419 4.1 .................................................................................... FLAMMABLE SOLID ....................................................... 172.420 4.2 .................................................................................... SPONTANEOUSLY COMBUSTIBLE .............................. 172.422 4.3 .................................................................................... DANGEROUS WHEN WET ............................................ 172.423 5.1 .................................................................................... OXIDIZER ........................................................................ 172.426 5.2 .................................................................................... ORGANIC PEROXIDE .................................................... 172.427 6.1 (material poisonous by inhalation (see § 171.8 of
this subchapter)).POISON INHALATION HAZARD .................................... 172.429
6.1 (other than material poisonous by inhalation) ........ POISON ........................................................................... 172.430 6.1 (inhalation hazard, Zone A or B) .............................. POISON INHALATION HAZARD .................................... 172.429 6.1 (other than inhalation hazard, Zone A or B) ............. POISON ........................................................................... 172.430 6.2 .................................................................................... INFECTIOUS SUBSTANCE 1 ......................................... 172.432 7 (see § 172.403) ............................................................ RADIOACTIVE WHITE-I ................................................. 172.436 7 ....................................................................................... RADIOACTIVE YELLOW-II ............................................. 172.438 7 ....................................................................................... RADIOACTIVE YELLOW-III ............................................ 172.440 7 (fissile radioactive material; see § 172.402) ................. FISSILE ........................................................................... 172.441 7 (empty packages, see § 173.428 of this subchapter) .. EMPTY ............................................................................ 172.450 8 ....................................................................................... CORROSIVE ................................................................... 172.442 9 ....................................................................................... CLASS 9 .......................................................................... 172.446
1 The ETIOLOGIC AGENT label specified in regulations of the Department of Health and Human Services at 42 CFR 72.3 may apply to packages of infectious substances.
[Amdt. 172–123, 55 FR 52593, Dec. 21, 1990, as amended at 56 FR 66255, Dec. 20, 1991; Amdt. 172–
151, 62 FR 1228, Jan. 8, 1997; 64 FR 10776, Mar. 5, 1999; 64 FR 51918, Sept. 27, 1999; 69 FR 3668,
Jan. 26, 2004; 69 FR 64471, Nov. 4, 2004; 78 FR 60753, Oct. 2, 2013]
§ 172.400a Exceptions from labeling. (a) Notwithstanding the provisions of
§ 172.400, a label is not required on— (1) A Dewar flask meeting the re-
quirements in § 173.320 of this sub-chapter or a cylinder containing a Di-vision 2.1, 2.2, or 2.3 material that is—
(i) Not overpacked; and (ii) Durably and legibly marked in
accordance with CGA C–7, Appendix A (IBR; see § 171.7 of this subchapter).
(2) A package or unit of military ex-plosives (including ammunition) shipped by or on behalf of the DOD when in—
(i) Freight containerload, carload or truckload shipments, if loaded and un-loaded by the shipper or DOD; or
(ii) Unitized or palletized break-bulk shipments by cargo vessel under char-
ter to DOD if at least one required
label is displayed on each unitized or
palletized load. (3) A package containing a hazardous
material other than ammunition that
is—
(i) Loaded and unloaded under the su-
pervision of DOD personnel, and
(ii) Escorted by DOD personnel in a
separate vehicle.
(4) A compressed gas cylinder perma-
nently mounted in or on a transport
vehicle.
(5) A freight container, aircraft unit
load device or portable tank, which—
(i) Is placarded in accordance with
subpart F of this part, or
(ii) Conforms to paragraph (a)(3) or
(b)(3) of § 172.512.
(6) An overpack or unit load device in
or on which labels representative of
each hazardous material in the over-
pack or unit load device are visible.
(7) A package of low specific activity
radioactive material and surface con-
taminated objects, when transported
under § 173.427(a)(6)(vi) of this sub-
chapter.
(b) Certain exceptions to labeling re-
quirements are provided for small
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Pipeline and Haz. Matls. Safety Admin., DOT § 172.402
quantities and limited quantities in ap-plicable sections in part 173 of this sub-chapter.
(c) Notwithstanding the provisions of § 172.402(a), a Division 6.1 subsidiary hazard label is not required on a pack-age containing a Class 8 (corrosive) material which has a subsidiary hazard of Division 6.1 (poisonous) if the tox-icity of the material is based solely on the corrosive destruction of tissue rather than systemic poisoning. In ad-
dition, a Division 4.1 subsidiary hazard
label is not required on a package bear-
ing a Division 4.2 label. (d) A package containing a material
poisonous by inhalation (see § 171.8 of
this subchapter) in a closed transport
vehicle or freight container may be ex-
cepted from the POISON INHALATION
HAZARD or POISON GAS label or
placard, under the conditions set forth
in § 171.23(b)(10) of this subchapter.
[Amdt. 172–123, 55 FR 52594, Dec. 21, 1990]
EDITORIAL NOTE: For FEDERAL REGISTER ci-
tations affecting § 172.400a, see the List of
CFR Sections Affected, which appears in the
Finding Aids section of the printed volume
and at www.fdsys.gov.
§ 172.401 Prohibited labeling. (a) Except as otherwise provided in
this section, no person may offer for
transportation and no carrier may
transport a package bearing a label
specified in this subpart unless: (1) The package contains a material
that is a hazardous material, and (2) The label represents a hazard of
the hazardous material in the package. (b) No person may offer for transpor-
tation and no carrier may transport a
package bearing any marking or label
which by its color, design, or shape
could be confused with or conflict with
a label prescribed by this part. (c) The restrictions in paragraphs (a)
and (b) of this section, do not apply to
packages labeled in conformance with: (1) The UN Recommendations (IBR,
see § 171.7 of this subchapter); (2) The IMDG Code (IBR, see § 171.7 of
this subchapter); (3) The ICAO Technical Instructions
(IBR, see § 171.7 of this subchapter); (4) The TDG Regulations (IBR, see
§ 171.7 of this subchapter). (5) The Globally Harmonized System
of Classification and Labelling of
Chemicals (GHS) (IBR, see § 171.7 of
this subchapter). (d) The provisions of paragraph (a) of
this section do not apply to a pack-
aging bearing a label if that packaging
is: (1) Unused or cleaned and purged of
all residue; (2) Transported in a transport vehicle
or freight container in such a manner
that the packaging is not visible dur-
ing transportation; and (3) Loaded by the shipper and un-
loaded by the shipper or consignee.
[Amdt. 172–9, 41 FR 15996, Apr. 15, 1976, as
amended by Amdt. 172–75, 47 FR 44471, Oct. 7,
1982; Amdt. 172–77, 47 FR 54822, Dec. 6, 1982;
Amdt. 172–94, 49 FR 38134, Sept. 27, 1984;
Amdt. 172–100, 50 FR 41521, Oct. 11, 1985;
Amdt. 172–123, 55 FR 52594, Dec. 21, 1990;
Amdt. 172–132, 58 FR 50501, Sept. 27, 1993; 66
FR 8647, Feb. 1, 2001; 66 FR 45379, Aug. 28,
2001; 68 FR 75741, 75742, Dec. 31, 2003; 74 FR
2252, Jan. 14, 2009]
§ 172.402 Additional labeling require-ments.
(a) Subsidiary hazard labels. Each
package containing a hazardous mate-
rial— (1) Shall be labeled with primary and
subsidiary hazard labels as specified in
column 6 of the § 172.101 table (unless
excepted in paragraph (a)(2) of this sec-
tion); and (2)For other than Class 1 or Class 2
materials (for subsidiary labeling re-
quirements for Class 1 or Class 2 mate-
rials see paragraph (e) or paragraphs (f)
and (g), respectively, of this section), if
not already labeled under paragraph
(a)(1) of this section, shall be labeled
with subsidiary hazard labels in ac-
cordance with the following table:
SUBSIDIARY HAZARD LABELS
Subsidiary hazard level (packing
group)
Subsidiary Hazard (Class or Division)
3 4.1 4.2 4.3 5.1 6.1 8
I ........................... X *** *** X X X X II .......................... X X X X X X X III ......................... * X X X X X X
X—Required for all modes. *—Required for all modes, except for a material with a flash
point at or above 38 °C (100 °F) transported by rail or high-way.
**—Reserved ***—Impossible as subsidiary hazard.
(b) Display of hazard class on labels. The appropriate hazard class or divi-
sion number must be displayed in the
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Appendix J EMS-WI-SW010, Contractor Hazardous Waste Management
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Reference Number: EMS-WI-SW010
FORT RUCKER Environmental Management System
Revision Date: 15 SEP 16
Title: Contractor Hazardous Waste Management
Approved By: Misty Howell / Melissa Lowlavar
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1.0 PURPOSE This procedure defines the requirements for managing hazardous waste generated by contractors temporarily working on Fort Rucker. Control of EMS procedures is addressed in procedure EMS-P002, Document Control. 2.0 SCOPE This procedure applies to all contractors that generate hazardous waste who are working temporarily on the installation. Contractors working on the installation long-term as part of regular installation operations (i.e., aviation maintenance contractor, base service support contractor) should refer to management procedures within the Hazardous Waste Management Plan. 3.0 DEFINITIONS
TERM DEFINITION 90-HWAS Less than 90-day Hazardous Waste Accumulation Site Accumulation Start Date (ASD)
The accumulation start date is the date the first item is placed in the container.
Accumulation Threshold
The accumulation threshold is 55-gallons for hazardous waste or 1-quart for acutely hazardous waste.
ADEM Alabama Department of Environmental Management DPW-ENRD Directorate of Public Works, Environmental and Natural
Resources Division, located in Bldg 1121, telephone number 334-255-2541
Hazardous Waste
A solid waste that is not specifically excluded or exempted in ADEM Administrative Code 335-14-2-.01(4)(a)-(b) and that is a listed waste in ADEM Administrative Code 335-14-2 and/or exhibits a characteristic of hazardous waste as defined in ADEM Administrative Code 335-14-2-.03.
HWSAP Hazardous Waste Satellite Accumulation Point is where the hazardous waste is generated and collected in the work place.
Solid Waste Any garbage, refuse, sludge, liquid, semi-solid, or contained gaseous material resulting from industrial, commercial, mining, and agricultural activity. A material is a solid waste after it has been used for its intended purpose, when it is discarded by being abandoned, and sometimes when it is recycled.
Reference Number: EMS-WI-SW010
FORT RUCKER Environmental Management System
Revision Date: 15 SEP 16
Title: Contractor Hazardous Waste Management
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4.0 RESPONSIBILITIES
4.1 Contractors. It is the responsibility of each contractor to follow proper procedures for hazardous waste management in accordance with federal and state regulations and this work instruction. Contractors are responsible for paying any fines resulting from noncompliance, which may be as high as $37,500 per violation per day.
4.2 DPW-ENRD Responsibilities. DPW-ENRD will provide additional guidance
as necessary to help ensure compliance with hazardous waste regulations. DPW-ENRD will periodically perform inspections to validate conformance with this procedure. Updates to this procedure will be made by DPW-ENRD as necessary.
5.0 PROCEDURE
5.1 Contractors will identify all wastes that may be generated prior to starting work on the installation. The contractor will work with DPW-ENRD to assess whether any of the wastes that may be generated are hazardous wastes in accordance with ADEM regulations.
5.2 If it is determined that the contractor is expected to generate hazardous
waste, they must coordinate with DPW-ENRD prior to commencement of operations to set up a hazardous waste satellite accumulation point. If a hazardous waste is generated that was not part of the planning process, the contractor must immediately notify DPW-ENRD.
5.3 All contractors must follow federal and state regulations for management of
hazardous waste. This procedure is not a replacement for reading and following the regulations. This procedure and the flowchart in Attachment 2 provide a summary of the requirements for proper management for operations generally conducted on Fort Rucker.
5.4 Waste Accumulation Time.
a. All hazardous waste must be accumulated in a hazardous waste satellite accumulation point (HWSAP) that is at or near the point of generation and that is under the control of the operator. The HWSAP must be secured to prevent unauthorized access. The only waste that should go into the HWSAP container is waste determined by DPW-ENRD to be hazardous waste. If a different type of waste is generated then the contractor must immediately notify DPW-ENRD.
Reference Number: EMS-WI-SW010
FORT RUCKER Environmental Management System
Revision Date: 15 SEP 16
Title: Contractor Hazardous Waste Management
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b. Waste may be accumulated in a HWSAP until the container is filled or when the waste exceeds the accumulation threshold (55-gallons for hazardous waste or 1-quart for acutely hazardous waste). When the waste meets the accumulation threshold, the contractor must write the date the container is filled on the container as the accumulation start date.
c. If the accumulation threshold is reached or the container becomes full, the waste must be transferred to a less than 90-day hazardous waste accumulation site (90-HWAS). The contractor will need to have prepared a DD Form 1348-1A to turn in with the waste container at the 90-HWAS. Contact DPW-ENRD for assistance in preparing the DD Form 1348-1A.
d. There are five 90-HWAS. These 90-HWAS are located as follows: 1. Building 1207 on the main post 2. Near Building 1001 on the main post 3. Near the Lowe Army Heliport washrack 4. Near the Hanchey Army Heliport washrack 5. At Cairns Field between Hangars 30103 and 30104 In addition, there is a 180-day HWAS located at Shell Army Heliport that is managed as a 90-HWAS. Waste generated at Cairns and Shell must be turned in to the 90-HWAS and 180-day HWAS located at Cairns and Shell, respectively. At no time will the contractor transport hazardous waste across state roads as this is a violation of federal and state regulations.
5.5 Container Requirements. All hazardous waste must be accumulated in
containers that meet the following requirements: a. The container the waste is accumulated in must be a DOT approved
shipping container. b. The container must be sized appropriately for the amount of waste
to be generated. For example, if it is anticipated that only a gallon of waste will be generated, then use a 5 gallon container for accumulation instead of a 55 gallon drum. Fort Rucker must pay for waste disposal based on the size of the container not the weight. Contact DPW-ENRD for assistance if needed.
c. The container must be compatible with the type of waste being accumulated in the container.
d. DPW-ENRD will provide the contractor with prefilled out labels for the waste containers. Only put waste in the container that has been identified for that HWSAP.
e. Segregate containers of incompatible wastes: 1) Segregate reactive waste from ignitable waste
2) Segregate acids from caustics 3) Segregate corrosive waste from flammable waste
Reference Number: EMS-WI-SW010
FORT RUCKER Environmental Management System
Revision Date: 15 SEP 16
Title: Contractor Hazardous Waste Management
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4) Segregate oxidizers from all other wastes f. Containers of highly flammable liquid waste must be grounded. g. Keep containers closed unless actively adding or removing waste. h. Protect containers from direct sunlight and inclement weather. i. Maintain containers in good condition – free of rust, dents, holes, or
other defects that may compromise the integrity of the container. j. Situate containers on a pallet or other device that allows inspection
of all sides of the container. k. All containers of liquid waste must have secondary containment that
is able to hold the entire contents of the container plus 10% freeboard.
5.6 Inspection Requirements.
a. All containers that are in the work place accumulating hazardous waste over 7 days must be visually inspected weekly using USAACE Form 2725, HWSAP Inspection Checklist.
b. Any deficiencies noted during these inspections should be immediately corrected or submitted to supervisor for further action. Contractors should contact DPW-ENRD if they have questions regarding any deficiencies.
c. Personnel conducting the weekly inspections must attend one of Fort Rucker’s HWSAP Manager training classes. The training schedule can be found at the Sustainable Fort Rucker web site under the training tab.
5.8 Training Requirements. a. Federal and state regulations require that all personnel managing or
handling hazardous waste must be trained, either through classroom instruction or on-the-job-training, to respond to emergencies, protect the environment, and properly handle and dispose of hazardous wastes. The regulatory requirements for training may be found in the ADEM Administrative Code 335-14-5-.02(7).
b. Facility personnel whose duties have a direct effect on hazardous waste management and/or hazardous waste accumulation, whether by direct contact with the hazardous waste or through hazardous waste management activities, must receive training. Each person managing or handling hazardous waste must receive introductory and annual update hazardous waste training corresponding with his/her responsibilities. The annual update training must be completed within 365 days of the previous training.
c. The introductory training must be completed within six months of the date on which the employee begins work in a position requiring such training. Employees must be immediately and continuously
Reference Number: EMS-WI-SW010
FORT RUCKER Environmental Management System
Revision Date: 15 SEP 16
Title: Contractor Hazardous Waste Management
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supervised when performing hazardous waste duties until such training is completed.
d. At a minimum, all supervisors and managers of hazardous waste activities will take a training course that meets required standards. It is their responsibility to ensure that personnel working for them are trained either in formal courses or in-house using on-the-job-training and "shop level" classes to meet the regulatory requirements.
e. Training records must be maintained for three years after the personnel cease working for the contractor.
5.9 Spill Prevention and Response
a. Site Specific Spill Plan. Each organization using hazardous materials and generating hazardous waste must complete USAACE Form 2719, Site Specific Spill Plan, which is available on the Sustainable Fort Rucker website. It is also referenced in the Installation Spill Contingency Plan (ISCP). The organization must have a hard copy readily available at each location that stores hazardous material and/or hazardous waste.
b. Spill Response. In the event that hazardous material or hazardous waste spills or leaks, the contractor must notify the Fire Department (call 911). The contractor is responsible for ensuring it is properly cleaned up in accordance with guidance from the Fire Department and DPW-ENRD.
c. Spill residue that contains a hazardous material or hazardous waste should be managed in accordance with the requirements in Sections 5.3 and 5.4. If the waste is waiting for laboratory analysis, the container should be marked PENDING ANALYSIS, dated with the date the sample was taken and turned into the 90-HWAS.
d. Spill residue that is or may potentially be a hazardous waste must not be removed from the installation without a manifest signed by authorized personnel within DPW-ENRD.
6.0 REFERENCES AND FORMS Sustainable Fort Rucker website: http://www.fortrucker-env.com EMS-P002, Document Control Hazardous Waste Management Plan (HWMP) Installation Spill Contingency Plan (ISCP) EPA Form 8700-22, Uniform Hazardous Waste Manifest USAACE Form 2719, Site Specific Spill Plan USAACE Form 2725, HWSAP Inspection Checklist USAACE Form 2726, 90-HWAS Inspection Log DD Form 1348-1A
ATTACHMENT 1
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Contractor Hazardous Waste Procedures
Accumulate hazardous waste in DOT approved,
compatible container
Contact DPW-ENRD (334-255-1024) prior to starting work to obtain assistance with identifying waste and setting up HWSAP
Label container with pre-filled labels obtained
from DPW-ENRDstating “HAZARDOUS
WASTE” and contents of container
Store properly
Transfer waste to 90-HWAS when
accumulation threshold reached
Inspect weekly using USAACE
Form 2725
Segregate incompatible wastes
Ground highly flammable wastes
Keep elevated off floor (i.e., on a pallet)
Keep containers closed unless adding or removing waste
Protect from direct sunlight & inclement weather
Provide adequate secondary containment for containers of
liquid waste
“ACCUMULATION START DATE:______“ indicating date container was filled
Prepare DD Form 1348-A1 for turn in to 90-HWAS. Contact DPW-
ENRD for assistance.
Complete manifest with all required information
HWSAP accumulation threshold: 55-gal HW or 1-qt acute HW
Store hazardous waste in HWSAP in accordance with Federal & State Regulations
Segregate reactive HW from ignitable HW
Segregate acids from caustics
Segregate corrosive HW from flammable HW
Segregate oxidizers from all other wastes
No leaks, dents, corrosion, bulging, or noticeable spills
Overpack any leaking containers
Immediately clean up any spills
Contact DPW-ENRD to arrange for signing manifest
Complete HW label and place on container
Mark container with appropriate hazard markings (49 CFR
172.400)
Proper DOT Shipping Name
Fort Rucker (Contractor name), building number, &
phone number
Fort Rucker EPA ID # Main Post AL6 210 020 776
Cairns AL9 210 090 040Shell AL2 210 090 039
Applicable Waste Codes
The statement, “FEDERAL LAW PROHIBITS IMPROPER
DISPOSAL. IF FOUND, CONTACT THE NEAREST
POLICE OR PUBLIC SAFETY AUTHORITY OR THE US
ENVIRONMENTAL PROTECTION AGENCY.”
Waste must be removed within 3 days of reaching accumulation
thresholdMaintain containers in good
condition
Appendix K EMS-WI-SW001, Waste Turn-In Procedure
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Reference Number: EMS-WI-SW001
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Waste Turn-In Procedure
Approved By: Misty Howell / Melissa Lowlavar
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1.0 PURPOSE This procedure defines the requirements for turning in solid wastes for management by Defense Logistics Agency Disposition Service (DLADS). Control of EMS procedures is addressed in procedure EMS-P002, Document Control. 2.0 SCOPE This procedure applies to all operations involving solid waste with hazardous constituents, including all activities and tenants that generate, recycle or reclaim waste, including those activities located at facilities outside the contiguous boundary of Fort Rucker. The requirements of this procedure are applicable to all military, civilian and contract personnel at Fort Rucker. 3.0 DEFINITIONS
TERM DEFINITION DLADS Defense Logistics Agency Disposition Service DPW-ENRD Directorate of Public Works, Environmental and Natural Resources
Division, located in Bldg 1121, telephone number 334-255-1024. HMCC Hazardous Material Control Center, located in Bldg 1315, telephone
number 334-598-1311. 90-HWAS Less Than 90-Day Hazardous Waste Accumulation Sites (also applies
to the less than 180-Day site located at Shell) HWMP The Fort Rucker Hazardous Waste Management Plan documents
personnel and procedures to ensure each step in the "cradle-to-grave" management of hazardous wastes is carried out in a consistent manner and in accordance with regulatory requirements. Procedures are either referenced or included in this HWMP, as necessary, to provide documented hazardous waste management instructions, from the time of waste generation until it is transported offsite for reuse or disposal.
4.0 RESPONSIBILITIES It is the responsibility of each waste generator to follow these procedures.
Reference Number: EMS-WI-SW001
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Waste Turn-In Procedure
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5.0 PROCEDURE 5.1 Turn-In Document
5.1.1 A DD Form 1348-1A is to be completed for all containers turned in
for waste disposal, recycle or reclamation. 5.1.2 The DD Form 1348-1A may be obtained from DPW-ENRD or the
HWMP. 5.1.3 Use the following instructions to complete the DD Form 1348-1A.
Using the areas marked on the example of DD Form 1348-1A below, fill in the numbered areas with the following information: Item 1. Box #2 “Ship From”: Type the name of the generator, or the name of the agency who created the waste, and “Ft. Rucker”. Item 2. “Units Issued”: To designate if the containers are drums or boxes, type “DR” for drums or “BX” for box. Item 3. “Qty”: Type the number of containers being shipped with this document. i.e. Type “2” for two drums of waste to be shipped. (One TYPE of waste per document.) Item 4. “Fund”: Type the number provided to your agency by the Hazardous Waste Program Manager. Item 5. “Dollars CTS”: Type the cost per container from the correct waste profile. NOTE: Item 5 is located at the top of the form and at the bottom. Enter the cost in both locations. Please reference the most recent waste profile list provided by the Hazardous Waste Program Manager. Item 6. Box 4 “Mark For”: Type “NON-RCRA” for Non-RCRA waste, “HAZARDOUS WASTE” for hazardous waste, or “UNIVERSAL WASTE” for universal waste as designated on the applicable waste profile. Please reference the most recent waste profile list provided by the Hazardous Waste Program Manager. Item 7. “Document Number and Suffix”: Unless your organization has a different code (check with Hazardous Waste Program Manager) type “W31BMV” then enter the 4-digit Julian Date followed by the number “1525”. With each additional DD Form 1348-1A created in a single day, add 1 to the number “1525”. i.e. The first document of
Reference Number: EMS-WI-SW001
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Waste Turn-In Procedure
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the day is “W31BMV-6230-1525”, the second document is “W31BMV-6230-1526”, and so on.
Item 8. “DOT Shipping Name”: Copy the DOT Shipping name exactly as it appears on the waste profile list. Please reference the most recent waste profile list provided by the Hazardous Waste Program Manager. Item 9. “National Stock Number (NSN)”: Copy the National Stock Number exactly as it appears on the waste profile list. Please reference the most recent waste profile list provided by the Hazardous Waste Program Manager. Item 10. “Bill To”: Type the number provided to your agency by the Hazardous Waste Program Manager. Item 11 a. “Item”: Copy the waste name exactly as it appears on the waste profile list. Please reference the most recent waste profile list provided by the Hazardous Waste Program Manager. Item 11b. “Waste Codes”: If the waste is a Hazardous Waste, then copy the waste codes exactly as it appears on the waste profile list. If the waste Universal Waste or Non-RCRA Waste, enter “n/a”. Please reference the most recent waste profile list provided by the Hazardous Waste Program Manager. Item 12. “TY CONT”: Use the following list to enter the correct container type and size code for the waste.
DM (drum, metal) + capacity (5, 40, 55 gal) DF (drum, fiber or plastic) CF (carton, fiber) = box CW (crate, wooden) = pallet Item 13. “Total Weight”: If your agency has a properly calibrated and maintained scale, then please enter the weight of the waste container. However, this item is optional and the container will be weighed at turn-in even if a weight has been entered in this space. Item 14. “CLIN”: Copy the CLIN exactly as it appears on the waste profile list. Please reference the most recent waste profile list provided by the Hazardous Waste Program Manager.
Reference Number: EMS-WI-SW001
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Waste Turn-In Procedure
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Item 15. “Profile Number”: Copy the profile number exactly as it appears on the waste profile list. Please reference the most recent waste profile list provided by the Hazardous Waste Program Manager. Item 16. “EPA ID”: Enter the EPA ID code, as listed at the top of the Waste Profile List, for the area where the waste was produced. i.e. If the waste was produced within the Main Cantonment Area, Enter “AL6210020776.” Item 17. “Certified By”: Leave blank. To be signed at turn-in by the person accepting the waste at the HMCC.
Additional Information: The “POC” listed on the lower right-hand side of the form is the name of the person who created the document. This person must also sign the “Inspected By” line at the bottom right-hand of the form. You may NOT create DD Form 1348-1A documents for waste turn-in unless you have completed the proper training. DPW-ENRD provides the required training classes each quarter. See http://fortrucker-env.com to register for classes.
Reference Number: EMS-WI-SW001
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Waste Turn-In Procedure
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Reference Number: EMS-WI-SW001
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Waste Turn-In Procedure
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5.2 Activities Located within the Boundary of Fort Rucker For activities located within the physical boundary of Fort Rucker generating waste with hazardous constituents, the following applies:
5.2.1 Turn-in of waste containers will occur Thursday morning between
0900 and 1130 at Bldg 1207, or may be scheduled for other days/times by appointment if necessary. The original and two copies of the completed DD Form 1348-1A are to accompany waste containers being generated for turn-in at the 90-Day Hazardous Waste Building 1207. Note that the generator of the waste is responsible for completing the form correctly and obtaining required/authorized signatures. 5.2.1.1 One copy of the DD Form 1348-1A will be signed by the
HMCC Waste Manager/Representative and returned to the customer.
5.2.1.2 One copy of the DD Form 1348-1A will be attached to the respective container. If more than one container of the same type is noted, the form will be attached to the one with the oldest accumulation start date, with the document number being written on all applicable containers.
5.2.2 HMCC will provide original DD Forms 1348-1A from each week’s turn-ins to DPW-ENRD prior to noon on Friday for each week.
5.3 Activities Located Outside the Boundary of Fort Rucker
For activities located outside the physical boundary of Fort Rucker generating waste with hazardous constituents, the following applies:
5.3.1 One copy of the completed DD Form 1348-1A will be provided to the
DPW-ENRD within one week of waste turn-in. Note that the generator of the waste is responsible for completing the form correctly and obtaining required/authorized signatures.
5.3.2 One copy of the DD Form 1348-1A is to be attached to the respective container. If more than one container of the same type is noted, the form will be attached to the one with the oldest accumulation start date, with the document number being written on all applicable containers.
5.4 HMCC Responsibilities
5.4.1 The Hazardous Waste Manager will ensure containers are not damaged prior to accepting into the 90-HWAS at Building 1207. Waste that is not properly labeled and identified or that is not properly
Reference Number: EMS-WI-SW001
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Waste Turn-In Procedure
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packaged and safe to handle will not be accepted. Containers that are found to be leaking, corroded, or otherwise deteriorated must be either transferred to a different container or over packed in a DOT-approved container prior to accepting.
5.4.2 Each DD Form 1348-1A will be reviewed for completeness and accuracy prior to receiving the waste into the 90-Day HWAS at Bldg 1207. Items found to be incorrect or incomplete are to be corrected by the generator prior to receiving the waste.
5.4.3 The HMCC will provide original documents to DPW-ENRD by noon each Friday. Should a holiday fall on Friday, all data will be turned in the next available work day.
5.5 DPW-ENRD Responsibilities DPW-ENRD will review DD Forms 1348-1A for accuracy and ensure waste information is transferred to DLADS for Delivery Orders as required.
6.0 FORMS AND RECORDS DD Form 1348-1A 7.0 REFERENCES EMS-P002, Document Control Hazardous Waste Management Plan
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Appendix L Hazardous Waste Profile
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_
(If Yes, Enter Reference Standards in Part 3, Block 6)
Oct 2006
DRMS FORM 1930, Oct 2006 (EF)
INSTRUCTIONS FOR DRMS FORM 1930 (Authority: DOD 4160.21-M, Chap. 10, par. D.2.a.(3))
PART I A. GENERAL INFORMATION (Required) WASTE PROFILE NUMBER – A unique number assigned to this waste stream for future reference. The preferred format is Generator DoDAAC + five digit serial number assigned by either the Generator or the DRMO. Any variation from this format must be approved by your DRMO. 1. GENERATOR NAME – Enter the name of the generating facility. (Should match official name associated with the EPA ID number). 2. FACILITY ADDRESS – Enter the address of generating facility listed in block A.1. 3. ZIP CODE – Enter the generating facility’s five or nine-digit Zip Code. 4. GENERATOR USEPA ID – Enter the 12-character, alpha-numeric descriptor issued by the USEPA to the facility identified in block A.1. (If not applicable, enter “NONE”) 5. GENERATOR STATE ID – Enter the descriptor issued by the Resident State to the facility identified in block A.1. 6. TECHNICAL CONTACT – Enter the name of the person to contact for more information about this waste. 7. TITLE – Enter the Technical Contact’s official title (e.g., “HW-Manager”, “Shop Chief”, etc.). 8. PHONE – Enter the Technical Contact’s telephone number B. WASTE INFORMATION (Required) 1. NAME OF WASTE – Enter a name that is generally descriptive of this waste (e.g., paint wastes, oil-water separator sludge, PCB-contaminated dirt, etc.) 2A. USEPA WASTE CODE(S) – List all that apply. If non-RCRA, enter “NONE” 2B. STATE/LOCAL/HOST NATION WASTE CODE(S) – List all that apply. If not applicable, enter “NONE”. 3. PROCESS GENERATING WASTE – List the specific process/operation or source that generates this waste (e.g., paint-booth spray, PCB spill, metal-plating operation, etc.) 4. PROJECTED ANNUAL GENERATIONS – The quantity of waste projected for turn-in annually. (preferably in pounds, but other units of measure may be used, e.g., gallons, kilograms, etc.) 5. MODE OF COLLECTION – Describe the method used to collect and store this waste stream (e.g., drums, tanks, roll-off, etc.) 6. DIOXIN WASTE? – Storage and disposal of Dioxin wastes requires special attention. If this waste is a USEPA-listed Dioxin waste, indicate “Yes”, and contact your DRMO representative for further instructions. 7. A. IS THIS WASTE RESTRICTED FROM LAND DISPOSAL? – Check “YES” or “NO” B. HAS AN EXEMPTION BEEN GRANTED? – If “Yes”, explain in Part II, block 6, at “Explain how and why these documents comply with RCRA requirements”. C. DOES THE WASTE MEET APPLICABLE TREATMENT STANDARDS ALREADY? If “Yes”, explain in Part II, block 6, at “Explain how and why these documents comply with RCRA requirements”.
PART II 1. MATERIAL CHARACTERIZATION (Optional unless otherwise indicated) 1. COLOR – Describe the color of the waste (e.g., blue, clear, varies, etc.) 2. DENSITY – The specific gravity of water is 1.0. Most organics are less than 1.0. Chlorinated solvents, most inorganics, and paint sludge are greater than 1.0. 3. BTU/LB – This entry may be required if you request that this waste be used as a fuel substitute. 4. ASH CONTENT – This entry may be required is you request recovery of used oil. 5. TOTAL SOLIDS – Content can be expressed as either a weight percentage, or dry-weight concentration (mg/kg). 6. LAYERING – Check applicable box. Multi-layered means more than two layers (e.g., oil/water/solvent/sludge). Bilayered means the waste is comprised of two layers which may or may not be the same phase (e.g., oil/water, solvent/sludge). Single phase means the waste is homogeneous. 2. RCRA CHARACTERISTICS (Required as applicable) PHYSICAL STATE – If the four boxes do not apply, a description should be entered after “Other”. IGNITABLE – Check this box if the waste meets the criteria listed at 40 CFR 261.21. FLASH POINT – For liquids, list the flash point, regardless of whether the waste is Ignitable(D001) or NOT. TOTAL ORGANIC CARBON (TOC) – Required for Ignitable Liquids CORROSIVE – Check this box if the waste is corrosive as defined in 40 CFR 261.22. - If applicable, include the PH reading in the space provided. (40 CFR 261.22 (a)(1). - If applicable, check the “Corrodes Steel” box. (40 CFR 261.22 (a)(2). REACTIVE – Indicate if the waste is reactive as defined in 40 CFR 261.23. If so, indicate the reason by checking the appropriate box. If other than one of the reasons provided, explain in detail at Part II, “Special Handling Requirements”. TOXICITY CHARACTERISTIC – If the waste exhibits the characteristic of toxicity, as defined in 40 CFR 261.24, check this box, and include the contaminant level in Part II, block 3.
3. CHEMICAL/MATERIAL COMPOSITION (Required as applicable) CAS # - Chemical Abstract Number. (Optional) May be used instead of the chemical name in the “Component” block. COMPONENT – List all chemical and material components and contaminants. - Examples of chemical components and contaminants:
• “PCB’s”, “ methanol”, “oil”, “endrin”, “sodium chloride”, “napthalene”, “gasoline”, etc. • applicable F-listed constituents; e.g., for waste numbers F001-F005, the waste constituents of concern are
the solvents themselves. • applicable Underlying Hazardous Constituents (UHCs). For certain characteristic waste numbers, D001-
D043, you may have to examine the waste components for UHCs. Look in 40 CFR, Table 268.40. If the treatment standard given includes the words “and meet 268.48 standards”, then you must indicate any UHCs present in the waste if they are present above the levels specified in part 268.48.
- Examples of material components and contaminants: water, dirt, sand, paint sludge, rags, etc. CONCENTRATION – Use this column for constituents of concern which do not exceed 10,000 ppm (1%). Indicate the concentration level in ppm or mg/L. RANGE – For components comprising greater than or equal to 1% of the total waste stream, estimate the range (in percent) in which the component is present. The total maximum values of the components must be greater than, or equal to 100%, including chemical and material components. 4. SHIPPING INFORMATION - Refer to 49 CFR 172 to complete this part. NOTE: Information provided in this portion of the waste profile is not meant to constitute a standard USDOT certificate given by a shipper offering a package to a transporter, but is needed to identify any other health and safety hazards, which are not readily apparent from the basic waste description. 5. SPECIAL HANDLING INFORMATION - Describe those hazards which you know or reasonably believe are or may be associated with short term or prolonged human exposure to this waste (29 CFR 1910.1200). If known, please identify any carcinogens present in this waste in excess of 0.1% (29 CFR 1910.1200(d)(4). Failure to make an entry in this part is considered to be a representation that you neither know nor believe that there are any adverse human health effects associated with exposure to this waste. Also include any additional information that will aid in the management of this waste. 6. GENERATOR CERTIFICATION (Required) CHEMICAL ANALYSIS – Attach a copy, if applicable (see Note below). USER KNOWLEDGE - User knowledge is appropriate when it can be documented (e.g., in-out logs, published information, MSDS, process production information, etc.). There is room provided to explain “what’ and “why” user knowledge is used in lieu of analysis. CERTIFICATION - Include the PRINTED NAME of the person providing the Certification Signature. SIGNATURE - An authorized representative of the generator must sign and date this certification on the completed Hazardous Waste Profile Sheet. DATE – Date signed by Certifier*. * This Hazardous Waste Profile Sheet (HWPS) may be used for subsequent turn-ins of the same waste stream, for a period of one year. If a turn-in date is more than a year past the Certification Date listed, the generator must either re-certify the HWPS, or provide a new HWPS, with the current date. See instructions at DOD 4160.21-M, Chapter 10, par. D.2.a.(3)(b).
If you require assistance completing this form, please contact your local DRMO
Appendix M Container Labels
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Appendix N USAACE Form 2730, Hazardous Material Authorization Request
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HAZARDOUS MATERIAL AUTHORIZATION REQUESTFor use of this form, see Hazardous Waste Management Plan; the proponent is DPW-ENRD
Employee Name Phone
Requesting Organization
Organization DoDAAC
National Stock Number Nomenclature
Part Number Military Specification
Container Size Preferred Container Type
One-Time Need Stocked Permanently
Location(s) where product will be used/ Work Zone
Date:Approved
YES NO
Site Supply Supervisor
Site EH&S Coodinator
DPW-ENRD
HMCC Manager
Justification (TM, Manufacturer’s Specification, etc):
Printed Name and ID number (if applicable)
I. Requestor Information
(Responsible Supervisor Name, ID, Organization, Telephone)
II. Responsible PartiesI CERTIFY THAT THE MATERIAL IS REQUIRED AS STATED ABOVE
Approving Activity Date Signature/Comments
Signature:
Special conditions for using chemical (if any):
Organization and Telephone:
Description of Product Use/Process (describe work activity by which material will be used. Identify method of application):
Frequency of UseUnit of Measure
USAACE FORM 2730 (rev 15JUN16)THIS IS A CONTROLLED DOCUMENT.
VERIFY THE LATEST VERSION ONLINE.
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Appendix O EMS-WI-SW009, Absorbent Continued Use Program
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Reference Number: EMS-WI-SW009
FORT RUCKER Environmental Management System
Revision Date: 9 SEP 16
Title: Absorbent Continued Use Program
Approved By: Misty Howell / Melissa Lowlavar
Page 1 of 3 This is a controlled document.
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1.0 PURPOSE This procedure defines the requirements for managing absorbent pads, socks, wipes, mop heads, pillows and gloves for continued use. Control of EMS procedures is addressed in procedure EMS-P002, Document Control. 2.0 SCOPE This procedure applies to all operations involved in managing absorbent materials for continued use. This procedure applies to all military, civilian and contract personnel that order, supply, process, store, use, and track absorbents for continued use on Fort Rucker. 3.0 DEFINITIONS
TERM DEFINITION Absorbent Materials Pads, socks, wipes, pillows, gloves, and mopheads AUL Authorized Use List DPW-ENRD Directorate of Public Works, Environmental and Natural
Resources Division, located in Bldg 1121, telephone number 334-255-2541
HMCC Hazardous Material Control Center, located in Bldg 1315, telephone number 334-598-1311
QVL Qualified Vendor List 4.0 RESPONSIBILITIES
4.1 DPW-ENRD 4.1.1 Ensure installation-wide adherence to established policies and
procedures for the absorbent continued use program. 4.1.2 Maintain tracking documents (USAACE Form 2732).
4.2 Absorbent Supplier / Processor
4.2.1 Ensure appropriate pick-up and delivery service to the absorbent users.
4.2.2 Process and transport contaminated or used absorbents in accordance with regulatory requirements.
4.2.3 Provide documentation as required by the absorbent continued use procedure.
Reference Number: EMS-WI-SW009
FORT RUCKER Environmental Management System
Revision Date: 9 SEP 16
Title: Absorbent Continued Use Program
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4.2.4 Provide certification documentation as required by an ADEM approved absorbent continued use process.
4.2.5 Handle absorbent materials as a valuable commodity.
4.3 HMCC 4.3.1 Receive absorbent requests from the absorbent user and place the
order with the absorbent supplier/processor. 4.3.2 Ensure absorbent supplier/processors are on the Qualified Vendor
List (QVL).
4.4 Absorbent User 4.4.1 Adhere to established policies and procedures for the absorbent
continued use program, including segregation of used products, weighing of used materials, etc.
4.4.2 Handle absorbent materials as a valuable commodity. 4.4.3 Provide tracking data on used absorbents using USAACE Form
2732, Continued Use Absorbents Tracking Document.
5.0 PROCEDURE
5.1 Order absorbent materials 5.1.1 The absorbent user requests on their approved AUL the quantity
and type of absorbent needed by the date specified by the supplier. Specific items available for order are included in the pick lists on USAACE Form 2732, Continued Use Absorbents Tracking Document.
5.1.2 HMCC places the absorbent order with the supplier/processor.
5.2 Deliver absorbent materials 5.2.1 Supplier/processor delivers the absorbent user’s order to pre-
designated delivery points. 5.2.2 Supplier/processor provides user with a copy of the delivery
document to include but not limited to the delivery date, delivery location, container contents, container weight and drum identification number.
5.3 Use of absorbent materials
5.3.1 All used absorbent materials must be handled in a responsible manner (i.e. they must be handled as a valuable commodity).
5.3.2 Used absorbent materials must be segregated and placed into the drums provided by the supplier/processor for return. User will ensure that all trash and other debris is kept out of the drums.
Reference Number: EMS-WI-SW009
FORT RUCKER Environmental Management System
Revision Date: 9 SEP 16
Title: Absorbent Continued Use Program
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5.3.3 All materials that are considered unserviceable after being returned from the supplier/processor must be managed as a waste.
5.4 Pick-up of absorbent materials
5.4.1 User will stage drums containing used absorbent materials for return at pre-designated pick-up points.
5.4.2 User will provide DPW-ENRD with drum identification numbers, deliver/pickup date, total weight and number of drums returned, using USAACE Form 2732, Continued Use Absorbents Tracking Document. This information should be provided to DPW-ENRD in a timely manner after the transaction has been completed.
5.5 DPW-ENRD will maintain tracking information for absorbent materials 5.6 Processing of absorbent materials at supplier facility
5.6.1 All used absorbent materials must be handled in a responsible manner (i.e. they must be handled as a valuable commodity).
5.6.2 All used absorbent materials must be processed for continued use in accordance with regulatory requirements.
5.6.3 All materials that are clearly unserviceable after use must be managed as a waste.
5.6.4 All items that are sent to the supplier/processor must be returned to Fort Rucker even if they are remnants.
5.6.5 The supplier/processor must ensure that absorbent materials are cleaned, segregated, and returned to the central activity of origination (i.e. absorbent materials coming from the Facilities Maintenance Contractor will be returned to Facilities Maintenance Contractor, absorbent materials from Aircraft Maintenance Contractor will be returned to Aircraft Maintenance Contractor, etc.).
6.0 FORMS AND RECORDS USAACE Form 2732, Continued Use Absorbents Tracking Document 7.0 REFERENCES EMS-P002, Document Control
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Appendix P USAACE Form 2732, Continued Use Absorbents Tracking Document
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CONTINUED USE ABSORBENTS TRACKING DOCUMENTFor use of this form, see EMS-WI-SW009; the proponent is DPW-ENRD
LocationOrganizationPOC
DRUM NUMBER
WEIGHT (LBS)
DRUM NUMBER
WEIGHT (LBS)
0 0 0 0
TOTAL
Comments
TURNED INRECEIVED OR TURNED
IN?
RECEIVEDABSORBENT TYPE DATE NOTES
USAACE FORM 2732 (rev 15JUN16)THIS IS A CONTROLLED DOCUMENT.
VERIFY THE LATEST VERSION ONLINE.
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Appendix Q EMS-WI-SW002, Used Battery Management
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Reference Number: EMS-WI-SW002
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Used Battery Management
Approved By: Misty Howell / Melissa Lowlavar
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1.0 PURPOSE This procedure defines the requirements for management of used batteries on Fort Rucker. Control of EMS procedures is addressed in procedure EMS-P002, Document Control. 2.0 SCOPE This procedure applies to all operations that generate, transport, and temporarily store used batteries prior to turn-in for recycling, including those activities located at facilities outside the contiguous boundary of Fort Rucker. The requirements of this procedure are applicable to all military, civilian and contract personnel at Fort Rucker. 3.0 DEFINITIONS/REFERENCES
TERM DEFINITION 90-HWAS Less Than 90-Day Hazardous Waste Accumulation Site Accumulation Start Date (ASD)
The accumulation start date is the date the first item is placed in the container.
DOT Department of Transportation DPW-ENRD Directorate of Public Works, Environmental and Natural Resources
Division, located in Bldg 1121, telephone number 334-255-1024. HMCC Hazardous Material Control Center, located in Building 1315,
telephone number 334-598-1311. HWMP The Fort Rucker Hazardous Waste Management Plan documents
personnel and procedures to ensure each step in the "cradle-to-grave" management of wastes with hazardous characteristics is carried out in a consistent manner and in accordance with (IAW) regulatory requirements. Procedures are either referenced or included in this HWMP, as necessary, to provide documented hazardous waste management instructions, from the time of waste generation until it is transported offsite for reuse or disposal.
HWSAP Hazardous Waste Satellite Accumulation Point IAW In Accordance With Universal Waste
Universal wastes are hazardous wastes that are subject to less stringent hazardous waste management regulations, particularly by allowing more time for accumulation of these wastes in order to facilitate appropriate recycling or disposal. Four types of waste are
Reference Number: EMS-WI-SW002
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Used Battery Management
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TERM DEFINITION covered under the universal waste regulations: batteries, lamps, mercury-containing equipment, and pesticides.
Used Battery
A device that produced electricity and may have several primary or secondary cells arranged in parallel or series. The typical batteries that are used at Fort Rucker are:
Alkaline and Carbon-Zinc (e.g., 9-volt, D, C, AA, AAA, alkaline button) – Managed as Non-Hazardous Waste
Lithium, Nickel-Cadmium (NiCd), Mercuric-Oxide (button and other), Nickel-Metal Hydride (NiMH), Silver Oxide, Silver-Zinc, Zinc-Carbon, Zinc Air – Managed as Universal Waste
Lead-acid – Managed as one-for-one exchange for recycling. 4.0 RESPONSIBILITIES It is the responsibility of each unit, organization or contractor working on Fort Rucker to follow these procedures. 5.0 PROCEDURE 5.1 Non-Hazardous Used Batteries
5.1.1 Used single-use dry cell Alkaline and Carbon-Zinc batteries (e.g., 9-volt, D, C, AA, AAA, alkaline button) will be managed as Non-Hazardous Waste.
5.1.2 Non-Hazardous used single-use dry cell Alkaline and Carbon-Zinc batteries (e.g., nine-volt, D, C, AA, AAA, alkaline button) batteries will be collected and segregated from Universal Waste batteries (e.g., Lithium, Mercury, NiCd) and Lead-Acid batteries in separate containers.
5.1.3 Accumulating Used Non-Hazardous Batteries: 5.1.3.1 Each unit, organization or contractor must collect the used single-
use dry cell Alkaline and Carbon-Zinc batteries in a DOT approved container with a closing lid.
5.1.3.2 The individual, spent, dry cell Alkaline and Carbon-Zinc batteries are not required to be separated. They may simply be containerized in a DOT approved container. See U.S. Department of Transportation Pipeline and Hazardous Materials Safety Administration clarification letter dated 23 Jun 2009 for additional information regarding this Non-Hazardous/Non-Regulated Waste.
5.1.3.3 The unit, organization or contractor will ensure each container has the proper label affixed. The label must identify the specific type of battery to be accumulated in the container (e.g., Non-Hazardous Waste Used Alkaline Batteries). The label must meet the following requirements:
Reference Number: EMS-WI-SW002
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Used Battery Management
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-all labels must be visible on the container; and -all labels must contain:
the words "Non-Hazardous Waste", and the words “Used Alkaline/Carbon Zinc Batteries”, and the accumulation start date (ASD) (the date the first used
battery was placed in the container). 5.1.4 The unit, organization or contractor is to coordinate the turn-in of the used
batteries with the HMCC Customer Service Representative at 598-1311. 5.1.5 HMCC personnel will remove the lid of each container before accepting
batteries to ensure co-mingling of battery types has not occurred. Used batteries that have not been properly segregated or properly packaged will not be taken.
5.1.6 All containers holding used batteries are to be maintained, closed (as defined by the container manufacturer), labeled, and in good condition. Spill equipment is to be near the used battery accumulation site. Management of these used battery accumulation areas is to be IAW the Installation's HWMP at all times.
5.2 Universal Waste Batteries
5.2.1 Used Lithium, NiCd, Mercuric-Oxide (button and other), NiMH, Silver Oxide, Silver-Zinc, Zinc-Carbon, and Zinc Air batteries will be managed as Universal Waste.
5.2.2 Accumulating Universal Waste Batteries: 5.2.2.1 Universal Waste batteries (e.g., Lithium, NiCd, Mercuric-Oxide,
NiMH, Silver Oxide, Silver-Zinc, Zinc-Carbon, and Zinc Air) will be collected and segregated in separate DOT approved containers with a closing lid.
5.2.2.2 Units, organizations or contractors are responsible for ensuring that all used batteries are properly separated by Universal Waste Battery types to prevent short-circuiting during storage and transportation. Universal Waste batteries will be separated by one of the following methods:
-placing batteries in the original inner package; -taping the positive end of the batteries; or, -by using plastic “baggies” to separate individual batteries. 5.2.2.3 The unit, organization or contractor will ensure each container has
the proper label affixed. The label must identify the specific type of battery to be accumulated in the container (e.g., Universal Waste for Lithium, Mercury, NiCd). The label must meet the following requirements:
-all labels must be visible on the container; and, -all labels must contain:
the words "UNIVERSAL WASTE", and
Reference Number: EMS-WI-SW002
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Used Battery Management
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the words describing the type of battery (e.g., “Lithium Batteries”, and
the accumulation start date (ASD) (the date the first used battery was placed in the container).
5.2.2.4 All containers holding used batteries are to be maintained, kept closed (as defined by the container manufacturer), labeled, and in good condition. Spill equipment is to be near the used battery accumulation site. Management of these used battery accumulation areas is to be IAW the Installation's HWMP at all times.
5.2.3 Turning In Universal Waste Batteries: 5.2.3.1 Universal Waste batteries must be turned in for disposal within six
months of the ASD, regardless if full or not. Containers of Universal Waste batteries for turn in are to be accompanied by a completed DD Form 1348-1A.
5.2.3.2 The unit, organization or contractor is to coordinate the turn-in of Universal Waste batteries with the HMCC Customer Service Representative at 598-1311.
5.2.4 HMCC personnel will remove the lid of each container before accepting batteries to ensure co-mingling of battery types has not occurred. Used batteries that have not been properly segregated or properly packaged will not be taken.
5.2.5 The HMCC will not accept batteries that have not been segregated or properly packaged to prevent short-circuiting.
5.3 Lead-Acid Batteries
5.3.1 Units, organizations or contractors will recycle used lead-acid batteries using the one-for-one exchange program. This program provides a one-for-one exchange of new lead-acid batteries for unserviceable lead-acid batteries.
5.3.2 Accumulating Lead-Acid Batteries for Recycling: 5.3.2.1 Both new and used lead-acid batteries should be stored in
covered areas on pallets or in a covered spill containment pallet. 5.3.2.2 Lead-acid batteries do not need to be labeled. 5.3.2.3 Draining batteries before collection is not necessary. 5.3.2.4 Although lead-acid batteries are not managed as Universal
Waste, the unit, organization or contractor should not accumulate the batteries for an extended period of time and should implement a method to demonstrate how long the lead-acid batteries have been stored between shipments.
Reference Number: EMS-WI-SW002
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Used Battery Management
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5.3.3 Recycling Used Lead-Acid Batteries: 5.3.3.1 Units, organizations or contractors are responsible for ensuring
that used lead-acid batteries are properly recycled using the one-for-one exchange program.
5.3.3.2 The one-for-one exchange program vendor supplies new batteries to organizations and picks up any used batteries that have been collected.
5.3.3.3 The vendor takes the entire lead-acid battery (including the electrolyte solution) and transports the batteries to a battery recycler for recycling.
5.3.3.4 If the vendor does not have a particular facility on their pickup route, the unit, organization or contractor may turn in their used lead-acid batteries to the HMCC.
5.3.3.5 The unit, organization or contractor is to coordinate the turn-in of used lead-acid batteries with the HMCC Customer Service Representative at 598-1311.
5.3.4 A battery acid spill kit is to be near the used lead-acid battery accumulation site. Management of these used battery accumulation areas is to be IAW the Installation's HWMP at all times.
5.4 Leaking or Damaged Batteries
5.4.1 Leaking or damaged Non-Hazardous and Universal Waste batteries will be segregated from intact used batteries by placing the leaking or damaged battery in a sealed plastic bag or wrapped with plastic and sealed using tape. Once sealed, the leaking or damaged battery may be placed in the appropriate collection container.
5.4.2 Lead-acid batteries that are leaking or are damaged (e.g., cracked case) cannot be returned to the vendor as part of the one-for-one exchange program. These batteries will be accumulated in a HWSAP and turned in to the 90-HWAS for disposal as hazardous waste.
5.4.3 Units, organizations and contractors will have spill equipment and training to safely and efficiently clean up minor spills and releases of battery electrolyte solutions IAW the Installation Spill Contingency Plan.
5.4.4 Personnel should collect the clean-up wastes in an approved non-metal container or a metal container with an appropriate liner. Wastes from the clean-up of electrolyte solution will be managed and disposed of as hazardous waste IAW the HWMP.
6.0 FORMS AND RECORDS DD Form 1348-1A Inspection Records
Reference Number: EMS-WI-SW002
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Used Battery Management
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7.0 REFERENCES EMS-P002, Document Control 49 CFR Parts 171-180 US DOT Battery Clarification Letters Dated April 3, 2009, June 23, 2009, and November 25, 2009 DOD 4160.21-M, Chapters 4 and 10 Hazardous Waste Management Plan Installation Spill Contingency Plan
Appendix R EMS-WI-SW007, Management of Used Oil and Fuel Filters
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Reference Number: EMS-WI-SW007
FORT RUCKER Environmental Management System
Revision Date: 9 SEP 16
Title: Management of Used Oil and Fuel Filters
Approved By: Misty Howell / Melissa Lowlavar
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1.0 PURPOSE This procedure defines the requirements for managing used oil filters and used fuel filters from vehicle maintenance or equipment shops on Fort Rucker. Control of EMS procedures is addressed in procedure EMS-P002, Document Control. 2.0 SCOPE This procedure applies to all vehicles and equipment operations that generate used oil and fuel filters, including those activities located at facilities outside the contiguous boundary of Fort Rucker’s main cantonment area. The requirements of this procedure are applicable to all military, civilian, tenant, and contract personnel at Fort Rucker utilizing installation resources to manage these waste streams. Tenants or contractors utilizing a separate contractor for POL disposal/recycling should coordinate with DPW-ENRD if their operations make it necessary to deviate from this procedure. 3.0 DEFINITIONS
TERM DEFINITION DPW-ENRD Directorate of Public Works, Environmental and Natural Resources
Division, located in Building 1121, telephone number 334-255-1024.HMCC Hazardous Material Control Center, located in Building 1315,
telephone number 334-598-1311. HWMP Hazardous Waste Management Plan - documents personnel and
procedures to ensure each step in the "cradle-to-grave" management of hazardous or other special wastes is carried out in a consistent manner and in accordance with regulatory requirements. Procedures are either referenced or included in the HWMP, as necessary, to provide documented hazardous and other special waste management instructions, from the time of waste generation until it is transported offsite for reuse or disposal.
4.0 RESPONSIBILITIES
4.1 It is the responsibility of each activity to follow proper procedures in accordance with this work instruction. Any deviation from this procedure due to utilization of a different disposal/recycling contractor should be coordinated with DPW-ENRD to ensure continued environmental protection.
Reference Number: EMS-WI-SW007
FORT RUCKER Environmental Management System
Revision Date: 9 SEP 16
Title: Management of Used Oil and Fuel Filters
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4.2 DPW-ENRD responsibilities include periodically performing waste and
recycling drum surveys to validate conformance with this procedure. DPW-ENRD will conduct formal inspections as described in EMS-P006, Internal Auditing.
5.0 PROCEDURE
5.1 Management of Used Oil Filters 5.1.1 Non-metal filters (from all engines except gasoline) must be drained
of free flowing liquid, then may be disposed in regular trash. 5.1.2 Metal filters:
5.1.2.1 Metal filters may be returned to the HMCC directly or placed in designated blue totes for pick up by HMCC delivery personnel.
5.1.2.2 Metal filters will be drained, crushed and recycled by the HMCC. The HMCC will do the following: (a) Remove free-flowing oil through gravity and hot-drain into
proper used oil container. (b) Crush filters in a suitable machine so that the scrap metal
can be recycled and the used oil captured and transferred into the used oil accumulation container or tank (labeled “used oil”).
(c) Place crushed metal filters into collection containers for scrap metal recycling.
(d) Do not place any filters in the scrap metal collection containers unless they have been crushed.
(e) Check bottom of collection container for free liquid. Pump out or absorb any oil that has accumulated to avoid a leak or spill. It is recommended that collection containers be lined with absorbent pads to absorb residual oil from filters once crushed.
(f) Any containers of used filters awaiting crushing must be marked with the words “Used Oil Filters”. Additional words may also be used in conjunction with “Used Oil Filters” if desired for clarity, such as “Used Oil Filters for Recycling”.
(g) All containers must be closed except when adding or removing filters.
(h) All used oil containers or tanks must also be marked “Used Oil” and managed per current procedures for used oil management.
Reference Number: EMS-WI-SW007
FORT RUCKER Environmental Management System
Revision Date: 9 SEP 16
Title: Management of Used Oil and Fuel Filters
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5.2 Management of Fuel Filters (all fuels except gasoline) 5.2.1 For all used F24 or diesel filters, handle per instructions for used metal
and non-metal oil filters above. 5.2.2 Drain filters and manage used fuel separately from used oil.
5.3 Management of Gasoline Filters
5.3.1 Drain into separate container designated for gasoline only until there is no free flowing liquid or seepage from filters.
5.3.2 Collect in container separately from other waste streams marked “used gasoline fuel filters – pending analysis”. Contact DPW-ENRD so that laboratory sampling and analysis of the filters can be conducted.
5.3.3 If laboratory testing confirms that they are below hazardous waste action levels, they may be disposed in regular trash after being drained of all free flowing liquid.
5.3.4 If laboratory testing confirms that they are hazardous waste, they will be managed per all existing Fort Rucker hazardous waste management procedures.
5.4 Management of Terne-Plated Filters
5.4.1 Different handling and disposal requirements may apply to filters from buses, semi-tractors, heavy equipment, or construction equipment. Generators of filters from these equipment types must contact DPW-ENRD to obtain specific guidance. The reason for this is to confirm if filters are terne-plated. Terne (a lead-tin alloy) serves as a plating on some larger filters which may require different handling as hazardous waste. Light-duty automobiles and trucks typically use non-terne-plated filters.
6.0 FORMS / RECORDS
DD 1348-1A, Issue Release/Receipt Document
7.0 REFERENCES EMS-P002, Document Control EMS-P006, Internal Auditing EMS-WI-SW001, Waste Turn-In Procedure Hazardous Waste Management Plan (HWMP) Alabama Administrative Code 335-14-17-.02(1)(c) 40 CFR 261.4(b)(13)
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Appendix S EMS-WI-SW003, Used Lamps Management
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Reference Number: EMS-WI-SW003
FORT RUCKER Environmental Management System
Revision Date 8 SEP 16
Title: Used Lamps Management
Approved By: Misty Howell / Melissa Lowlavar
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1.0 PURPOSE This procedure defines the requirements for management of used lamps on Fort Rucker. Control of EMS procedures is addressed in procedure EMS-P002, Document Control. 2.0 SCOPE This procedure applies to all Fort Rucker operations that generate used lamps, including those activities located at facilities outside the contiguous boundary of the installation. The requirements of this procedure are applicable to all military, civilian and contract personnel at Fort Rucker. 3.0 DEFINITIONS
TERM DEFINITION Accumulation Start Date (ASD)
The accumulation start date is the date the first item is placed in the container.
DPW-ENRD
Directorate of Public Works, Environmental and Natural Resources Division, located in Bldg 1121, telephone number 334-255-1024.
Environmental Officer / EPOC
The Environmental Officer / EPOC is the main contact within an organization for ensuring continued conformance with the EMS and compliance with regulatory requirements. These personnel are assigned in accordance with GC Policy Memo 13-35.
Green-Tipped Lamp
A fluorescent lamp with low mercury content. Typically, the lamp has green tips, green marking, or green writing stating “low mercury content” on the lamp.
HMCC Hazardous Material Control Center, located in Bldg 1315, telephone number 334-598-1311.
90-HWAS / 180-HWAS Less Than 90-Day/180-Day Hazardous Waste Accumulation Site
HWMP The Fort Rucker Hazardous Waste Management Plan documents procedures to ensure each step in the "cradle-to-grave" management of wastes with hazardous characteristics is carried out in a consistent manner and in accordance with (IAW) regulatory requirements. Procedures are either referenced or included in the HWMP, as necessary, to provide documented waste management instructions, from the time of waste generation until it is transported offsite for reuse or disposal.
IAW In Accordance With
Reference Number: EMS-WI-SW003
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Used Lamps Management
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TERM DEFINITION Used Lamps Used lamps, also referred to as "universal waste lamp", means
the bulb or tube portion of an electric lighting device. Examples of common universal waste electric lamps include, but are not limited to, fluorescent lamps of various sizes, high intensity discharge (HID), neon, mercury vapor, high pressure sodium, and metal halide lamps.
Universal Waste Universal wastes are hazardous wastes that are subject to less stringent hazardous waste management regulations, particularly by allowing more time for accumulation of these wastes in order to facilitate appropriate recycling or disposal. Four types of waste are covered under the universal waste regulations: batteries, lamps, mercury-containing equipment, and pesticides.
4.0 RESPONSIBILITIES It is the responsibility of each unit, organization or contractor working at Fort Rucker to follow these procedures. 5.0 PROCEDURE
5.1 Purchase 5.1.1 IAW Green Procurement Guidance, environmentally friendly items will be
purchased where feasible. Green-tipped lamps will be purchased/used where available.
5.1.2 The most common types of green-tipped lamps will be made available through Self Help, Building 1427, either one at a time replacement quantities, or by the box. Individual credit card holders are responsible for purchasing replacement green-tipped lamps where practical.
5.2 Management of Used Lamps:
5.2.1 All used lamps, including green-tipped lamps, will be managed as Universal Waste lamps.
5.2.2 Always open a new lamp box by the pull flap. Never cut off flaps or “window cut” boxes. When all new lamps are used and the box is empty, this box now becomes suitable for used lamp accumulation.
5.2.3 Used Lamp Management: 5.2.3.1 Lamps that are no longer usable are Universal Waste according to
the applicable regulations. 5.2.3.2 Accumulating used lamps:
(a) When a used lamp is first placed into a box or fiber drum, that container must be labeled (please see the HWMP for example
Reference Number: EMS-WI-SW003
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Used Lamps Management
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labels and verbiage). The label must meet the following requirements:
-all labels must be visible from the front of the box -all labels must be right side up -all labels must contain:
the words "UNIVERSAL WASTE", and the words “Used Lamps”, and the accumulation start date (ASD) (the date the first used
lamp was placed in the container). (b) Box(es) or fiber drums containing used lamps must be kept
closed except when lamps are being added to it. (c) Filling a used lamp box on a 30-45 degree angle will help in
placing lamps in layer fashion, allowing more to be placed in the box. Do not stand 4’ and 8’ boxes on their end.
(d) Lamps must be segregated by type and by size. For example, all 4-foot fluorescent lamps should be in a separate box from 8-foot fluorescent lamps, from compact fluorescent lamps (CFLs), etc.
(e) Individual used lamps or partially-filled containers (boxes or fiber drums) may be turned in to the HMCC, each work day between 0730 and 1600.
(f) Full boxes or fiber drums of used lamps are to be accompanied by a completed DD Form 1348-1A, including a total bulb count. No container should be maintained longer than 6-months from the ASD, regardless if full or not. Note that full used lamp containers may be turned in to the Cairns 90-HWAS, the Shell 180-HWAS or the Fort Rucker 90-HWAS (Bldg 1207) on Thursdays or by appointment by calling the HMCC at 334-598-1311.
5.3 Broken Mercury-Containing Used Lamp Clean-Up
When handling used lamps, use caution to avoid breaking the lamps as mercury will be released into the atmosphere. If a mercury-containing lamp is broken, the lamp(s) should be managed as hazardous waste. Please reference the HWMP for detailed management procedures. Note that your units, organizations or contractors Environmental Officer, EPOC, or Hazardous Waste Manager are typically the only individuals trained within your organization to manage a hazardous waste. If one of these individuals is not available to clean up the broken mercury lamp, please notify the Fire Department (911) and the Service Order Desk (255-9041).
If a lamp breaks, follow the procedure below: 5.3.1 If not trained in hazardous waste cleanup, please call 911 and the Service
Order Desk 255-9041 for assistance. Note that if the lamp is green-tipped
Reference Number: EMS-WI-SW003
FORT RUCKER Environmental Management System
Revision Date: 8 SEP 16
Title: Used Lamps Management
Page 4 of 4 This is a controlled document.
Verify the latest version online.
any individual may clean-up the broken glass since little mercury remains. If one cannot determine if the lamp is a low mercury lamp, the broken lamp is to be managed as a mercury-containing lamp.
5.3.2 Keep all people away from the breakage area so mercury-containing powder is not tracked into other areas. Mercury may be bound to the broken glass and powder.
5.3.3 Air out the area for 15 minutes by opening a door or window to an outside area. Keep well ventilated. This allows mercury vapors to dissipate.
5.3.4 Assemble necessary supplies: latex gloves, tweezers, tape, index cards/cardboard, damp paper towels, and a plastic container.
5.3.5 Wearing the gloves, carefully pick up any broken glass and place in puncture resistant container. Tweezers can be used to safely pick up broken glass. Tape can be used to pick up small pieces of glass and powder residue left on spill surface.
5.3.6 Use two pieces of cardboard to push together remaining powder and fragments of glass. Finish cleanup by wiping with damp paper towels.
5.3.7 Important: Do Not Vacuum!! Mercury residue in the vacuum is heated up and can vaporize when the vacuum is used again.
5.3.8 After clean-up is complete, place contaminated clean-up equipment along with any other materials that came in contact with the mercury powder into the puncture resistant container.
5.3.9 Label all containers “Hazardous Waste-Contains Mercury.” 5.3.10 Store container(s) on a corrosion-proof surface, inside a structure that is
protected from the weather. 5.3.11 Complete a DD Form 1348-1A for turn-in as described in the Fort Rucker
HWMP and dispose as a hazardous waste. 5.3.12 Contact Misty Howell at 334-255-1024 for more information.
Spills of one pound (34 ml or approximately two tablespoons) or more are to be reported to DPW-ENRD at 255-1024 or 255-1657 immediately. 6.0 FORMS AND RECORDS DD Form 1348-1A 7.0 REFERENCES Hazardous Waste Management Plan EMS-P002, Document Control
Appendix T
USAACE Form 2719, Site Specific Spill Plan
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SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
USAACE FORM 2719 (24JUL15) Page 1 of 12 THIS IS A CONTROLLED DOCUMENT PREVIOUS EDITION IS OBSOLETE VERIFY THE LATEST VERSION ONLINE
POST THIS PAGE PROMINENTLY AT EACH HAZARDOUS WASTE SATELLITE ACCUMULATION POINT, 90-DAY HW SITE, HAZARDOUS MATERIAL STORAGE AREA, AND SPCC CONTAINER
STORAGE AREA
ORGANIZATION’S SPILL RESPONSE POINTS OF CONTACT
PRIMARY: PHONE:
ALTERNATE: PHONE:
APPROPRIATE FIRE DEPT / CRASH NUMBER:
LOCATION OF COMPLETE SITE SPECIFIC SPILL PLAN: TYPE OF MATERIAL / WASTE STORED (general description of what is stored in the area)
LOCATION OF MSDS/SDS / ADDITIONAL WASTE INFORMATION
LOCATION OF NEAREST SPILL KIT / SUPPLIES
Spill Response
Call 911 for all spills to the environment (water, soil, drains)
Remove the source of the spill
Envelop spilled material on ground
Absorb spilled material; clean up soil
Containerize used absorbent & soil
Transmit a report of the spill
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
USAACE FORM 2719 (24JUL15) Page 2 of 12 THIS IS A CONTROLLED DOCUMENT PREVIOUS EDITION IS OBSOLETE VERIFY THE LATEST VERSION ONLINE
MAINTAIN THE REMAINDER OF THE PLAN IN THE AREA DESIGNATED ON PG 1, WHICH MUST BE EASILY ACCESIBLE, AT EACH FACILITY WITH A HWSAP, 90-HWAS, HM STORAGE AREA, OR SPCC CONTAINER
STORAGE AREA
SECTION 1. ORGANIZATION IDENTIFICATION
Organization:
Commander/Supervisor:
Environmental Officer/EPOC:
Secondary POC:
Location/SPCC Plan Figure (i.e., South Fort Rucker)
Bldg. Number and/or Shop Name
Date plan prepared/updated:
Signature of Commander/Supervisor Signature of Environmental Officer/EPOC SECTION 2. PLAN REVIEW AND AMENDMENT
This plan will be reviewed for adequacy and accuracy and updated at least annually. Upon issuance of a new version of this EMS form, organizations may wait for their annual review to update their Site Specific Spill Plan to reflect any changes to this form. SECTION 3. PURPOSE This Site Specific Spill Plan provides policy, guidance, and procedures for the prevention, control, containment, and response to spills of oil products and hazardous substances within the organization’s facilities. It has been prepared in compliance with the requirements of the Spill Prevention, Control and Countermeasures (SPCC) Plan and the Installation Spill Contingency Plan (ISCP). This plan also meets the requirements for spill response procedures contained within the Hazardous Waste Management Plan (HWMP). SECTION 4. DEFINITIONS A. Acronyms
90-HWAS Less than 90-Day Hazardous Waste Accumulation Site ADEM Alabama Department of Environmental Management DPW Directorate of Public Works EMS Environmental Management System ENRD Environmental and Natural Resources Division EPOC Environmental Point of Contact
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
USAACE FORM 2719 (24JUL15) Page 3 of 12 THIS IS A CONTROLLED DOCUMENT PREVIOUS EDITION IS OBSOLETE VERIFY THE LATEST VERSION ONLINE
HWMP Hazardous Waste Management Plan HWSAP Hazardous Waste Satellite Accumulation Point ISCP Installation Spill Contingency Plan MSDS Material Safety Data Sheet OSC On Scene Coordinator RCRA Resource Conservation and Recovery Act RQ Reportable Quantity SDS Safety Data Sheet SPCC Spill Prevention, Control, and Countermeasures SWPPP Stormwater Pollution Prevention Plan
B. Spill: A spill is broadly defined as a release of any kind of a petroleum product (fuel or oil) or hazardous substance to the environment. Spill reaction is based largely on the nature, quantity, and location of the material spilled. For the purposes of this plan, the following spill classifications will apply:
1. Small Priming Spill - A spill that covers less than 18 inches in all directions.
2. Small Spill - A spill that extends less than 10 feet in any direction, covers less than 50 square feet, and is not continuous.
3. Large Spill - A spill that extends farther than 10 feet in any direction, covers an area in excess of 50 square feet or is continuous (e.g., a leaking tank).
C. Significant spill: A significant spill is defined as an uncontained release to the land,
water or air in excess of any of the following quantities:
1. For hazardous waste or hazardous material identified as a result of inclusion in the Title III List of Lists (ISCP Appendix H), any quantity in excess of the reportable quantity (RQ) listed in the Title III List of Lists.
2. For oil or liquid or semi-liquid hazardous material or hazardous waste, in excess of 400 liters (110 gallons). For purposes of reporting to Federal, State, and local authorities, a reportable oil spill is defined as any spill that exceeds 25-gallons (ADEM requirement) or that reaches a stream, creek, river or any other body of water in harmful quantities (see definition above).
3. For other solid hazardous material, in excess of 225 kg (500 lbs.).
4. For combinations of oil and liquid, semi-liquid and solid hazardous materials or hazardous waste, in excess of 340 kg (750 lbs.).
5. If a spill is contained inside an impervious berm, or on a nonporous surface, or inside a building and is not volatilized and is cleaned up, the spill is considered a contained release and is not considered a significant spill.
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
USAACE FORM 2719 (24JUL15) Page 4 of 12 THIS IS A CONTROLLED DOCUMENT PREVIOUS EDITION IS OBSOLETE VERIFY THE LATEST VERSION ONLINE
6. For releases to the air, substances in (but not limited to) the Title III List of Lists in quantities that may as a result of short-term exposure cause death, injury or property damage due to their toxicity, reactivity, flammability, volatility or corrosivity.
SECTION 5. RESPONSIBILITIES A. Commander/Supervisor:
1. Implement this plan.
2. Review and sign the plan when it is prepared or updated.
3. Appoint an organization Environmental Officer/EPOC to carry out the duties associated with this plan.
B. Environmental Officer/EPOC:
1. Update and maintain this plan as needed based on changes in organization mission, function, and facilities. At a minimum, this plan will be updated annually.
2. Requisition, store, maintain and issue materials used for the cleanup of spills within the organization’s area.
3. Respond to, evaluate, classify and record data on all spills within the unit.
4. Contact the Fort Rucker Fire Department for all oil spills and spills of hazardous substances released to the land, water or air. Provide all information concerning the spill event as well as any determinations made on the classification of the spill.
5. Document all spills within the organization and maintain an appropriate file.
6. Develop and implement a training program for organizational personnel.
7. Conduct inspections required by the SPCC Plan and the Hazardous Waste Management Plan.
SECTION 6. ORGANIZATIONAL ACTIVITIES / POTENTIAL SPILL SOURCES Attach hazardous material inventory, SPCC inventory, and/or waste profile information or fill out the following table with applicable information ONLY for materials/wastes stored in the facility listed in Section 1. Do NOT attach AUL or waste profiles for materials/wastes that are stored in facilities covered by another Site Specific Spill Plan.
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
USAACE FORM 2719 (24JUL15) Page 5 of 12 THIS IS A CONTROLLED DOCUMENT PREVIOUS EDITION IS OBSOLETE VERIFY THE LATEST VERSION ONLINE
MATERIAL / WASTE STORED CONTAINER
SIZE STORAGE LOCATION
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
USAACE FORM 2719 (24JUL15) Page 6 of 12 THIS IS A CONTROLLED DOCUMENT PREVIOUS EDITION IS OBSOLETE VERIFY THE LATEST VERSION ONLINE
SECTION 7. FACILITY DESCRIPTION
Describe the facility (i.e. steel frame, brick, square footage, year built, type of operation within building and outside the building, number and location of flammable storage, HWSAPs, etc.). Attach a map/drawing that shows storage locations (maps are available in the SPCC Plan and the SWPPP showing higher risk storage locations).
SECTION 8. SPILL PREVENTION
1. Use drip pans under all parked vehicles and equipment that leak.
2. Use drip pans under all hose connections that leak.
3. Close all valves before disconnecting/connecting any hoses.
4. Drain all parts before moving away from parts cleaning equipment.
5. Provide storage with secondary containment for all oil and hazardous substances stored in 55-gallon or larger containers.
6. Employ good housekeeping procedures to maintain work areas.
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
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SECTION 9. LOCATION AND DESCRIPTION OF SPILL RESPONSE EQUIPMENT Materials for cleanup of spills should be readily available. These materials should include items such as kitty litter, oil absorbent pads, dry sweep, oil socks/booms, shovel, and gloves. (ONLY include supplies stored in the facility listed in Section 1) A. Spill Containment Equipment:
B. Fire Control Equipment
C. Personal Protective Equipment
D. First Aid and/or Medical Supplies
E. Emergency Decontamination Equipment
F. Emergency Communication and Alarm System
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
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SECTION 10. POSSIBLE SPILL ROUTES
The following spill routes are possible within the organization’s area of responsibility (attach a figure/map as necessary – spill routes are depicted on figures in SPCC Plan and SWPPP for higher risk storage areas):
LOCATION DESCRIPTION
(i.e., shop name)
BLDG NUMBER
INSIDE OR OUTSIDE?
SPILL ROUTE (i.e., remain on the floor until
cleaned up; flow toward the south)
SECTION 11. SPILL RESPONSE / CLEANUP In the event of a spill the following actions should be taken. The order of the actions will depend on the existing conditions.
1. EVACUATE AREA, IF NECESSARY
2. NOTIFY THE FIRE DEPARTMENT, EXT 911 or 255-0044
3. NOTIFY SUPERVISOR , EXT
4. CHECK CAUSE AND STOP SOURCE OF SPILL, WHEN POSSIBLE, WITHOUT UNDUE RISK OF PERSONNEL INJURY.
5. MAKE SPILL SCENE OFF LIMITS TO UNAUTHORIZED PERSONNEL AND VEHICLES
6. RESTRICT ALL SOURCES OF IGNITION
7. COVER DRAINS IN AREA OF SPILL, WITHOUT UNDUE RISK OF PERSONNEL INJURY
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
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8. REPORT TO ON-SCENE-COORDINATOR (OSC) WITH MSDSs/SDSs
When notifying the fire department, the following information should be provided if known or can reasonably be determined.
1. Location, time, and type of incident (spill, fire, injury, etc.).
2. Name and quantity of spilled material and the rate of release.
3. Provide MSDS/SDS for spilled material, if available.
4. Direction of the spill, vapor, or smoke release.
5. Fire and/or explosion possibility.
6. Coverage area of spill and the intensity of any fire or explosion.
7. The extent of injuries, if any.
SECTION 12. SPECIAL PRECAUTIONARY MEASURES A. Designated Evacuation Route and Distance (attach map if necessary)
B. Specified Meeting Point
C. Consult MSDS/SDS for firefighting and first aid procedures. MSDS/SDS location:
SECTION 13. POSTING REQUIRMENTS A. The first page of the Site-Specific Spill Plan will be printed and will be posted in a
prominent place adjacent to each HWSAP, 90-HWAS, HM Storage Area, and SPCC Container Storage Area. The remainder of the plan will be placed in the location designated on page 1 within the building or shop so that everyone involved in working at the site will be able to access and implement its contents.
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
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B. A signed copy, along with the ISCP, will be maintained by the Environmental Officer/EPOC along with a listing of all applicable MSDS/SDS.
C. Documentation of spills to the ground or water is to be provided to the DPW-ENRD within 24-hours of the incident.
SECTION 14. INSPECTION PROGRAM A. The Environmental Officer/EPOC will conduct monthly inspections (weekly for used
products) on all oil containers 55-gallons or larger to ensure compliance with this plan, to identify deficiencies and to make recommendations on corrective actions required. These inspections will be documented using USAACE Form 2711 SPCC Container Inspection Form. Copies of all inspection forms will be forwarded to DPW-ENRD at the end of each month.
B. The HWSAP Manager or the 90-HWAS Manager will conduct inspections of all
hazardous waste containers to ensure compliance with this plan, to identify deficiencies and to make recommendations on corrective actions required. These inspections will be documented using USAACE Form 2725 Hazardous Waste Satellite Accumulation Point Inspection Checklist or USAACE Form 2726 Less than 90-Day Hazardous Waste Accumulation Site Inspection Log.
C. The Environmental Officer / EPOC may conduct inspections of all hazardous material
storage areas and potential stormwater issues using the applicable sections of USAACE Form 2717 Environmental Compliance Inspection Checklist. These inspections are conducted quarterly by DPW-ENRD, but organizations should consider conducting self-inspections to help ensure continued compliance.
SECTION 15. TRAINING PROGRAM A. The Environmental Officer/EPOC will receive training on the SPCC Plan and ISCP
from the DPW-ENRD within six months of assignment of duties and at least annually thereafter.
B. Training on the organization’s Site Specific Spill Plan, the Fort Rucker SPCC Plan, and
the Fort Rucker ISCP are required for all oil handling personnel. 1. This training should include:
a. Types of hazardous and toxic substances used in the organization. b. Methods of retaining spills. c. Methods of recovering spilled materials. d. Disposition of contaminated soil, absorbent material and recovered
substance. e. Restoration of contaminated areas to their former condition.
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
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2. All such personnel will receive this training within 30 days of assignment of appropriate duties and at least annually thereafter.
C. Training is required for personnel who handle hazardous waste and for managers and supervisors of personnel who handle hazardous waste, including those who maintain and operate HWSAPs / 90-HWAS (HWSAP / 90-HWAS Managers).
1. Initial personnel training is required to be completed within six months of the
individual being assigned to hazardous waste handling duties. 2. Training will focus on how to safely manage and operate a HWSAP / 90-HWAS.
It must enable employees involved with hazardous waste operations to perform their duties without endangering themselves or other employees. Emphasis should be given to the emergency response, use of protective equipment and clothing, recognition of hazardous waste, hazards of waste encountered, and an overview of RCRA regulations relating to employees.
3. DPW-ENRD offers a two hour HWSAP Manager Course and a two hour 90-
HWAS Manager Course that are required annually for all personnel assigned as a primary or alternate HWSAP / 90-HWAS manager.
D. The Environmental Officer/EPOC will maintain records of training. Records on
individuals will be maintained on file for a minimum of three years after departing the organization. A copy of the individual’s training record may be provided to the individual upon their departure.
SECTION 16. YEARLY EXERCISE This plan will be exercised within the organization at least yearly through the staging of a mock spill. The Environmental Officer/EPOC will develop, supervise, evaluate, and document the exercise to test the understanding by the organization of the plan, their ability to appropriately respond to a spill, and the overall effectiveness of the plan. SECTION 17. DOCUMENTATION A. All spills will be documented/reported using USAACE Form 2718 Spill Notification
Report. These records will be maintained for a minimum of three years. B. All inspections conducted in accordance with the ISCP, the SPCC Plan, and the
HWMP will be documented using appropriate EMS forms. These records will be maintained for a minimum of three years.
C. All training records will be maintained for a minimum of three years.
SITE SPECIFIC SPILL PLAN For use of this form, see the Installation Spill Contingency Plan; the proponent is DPW-ENRD
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D. The Environmental Officer/EPOC will develop and maintain an Environmental Binder relating to environmental activities within the organization. The file will contain all information specified in EMS-WI-EM001, Environmental Binder Work Instruction.
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