Pollution Prevention Opportunity Assessments

April 2000 - TI#21448
Introduction
Important Terms
Drivers for Conducting P2OA's
The Waste Management Hierarchy
Conducting a P2OA
Post P2OA Activities
For More Information
References


Introduction
The Air Force is continually looking for new and innovative ways to prevent and reduce pollution to the environment. Pollution prevention (P2) can be defined as a process designed to curtail the use of hazardous materials and the release of pollutants into the environment to "as near zero" as is technically and economically feasible. Many federal, Department of Defense (DoD), and Air Force guidance documents require the implementation of P2 practices as a means of preventing future pollution that would eventually require remediation, and to reduce the burden of complying with various environmental regulatory requirements. One of the principal P2 practices employed is the Pollution Prevention Opportunity Assessment, also known as PPOA or P2OA. The P2OA is a systematic procedure that is used to identify opportunities for reducing or eliminating the generation of waste, thereby lessening potential adverse impacts to the environment. The final outcome of a P2OA should be the identification of all pollutant sources, examination of the total waste generation by type and volume, and finally, a determination of the most economical and practical options.

Several policy memorandums issued by the Office of the Air Force Civil Engineer, and the planned update of Air Force Instruction (AFI) 32-7080, "Pollution Prevention Program," have cast P2 as the primary method by which the Air Force will achieve compliance with environmental program requirements. Conducting P2OAs is seen as an important and integral component of this "compliance through pollution prevention" mandate. The purpose of this fact sheet is to provide Air Force personnel with a basic understanding of the P2OA process. Included is a summary of the policy drivers for conducting P2OAs, general guidance on how to set-up and conduct an assessment, and sources of additional information and assistance.


Important Terms
Alternatives: Ways of reducing adverse effects of hazardous materials (HAZMAT). Alternatives (also called opportunities), as applied to HAZMAT decision-making, include, but are not limited to:
  • Substituting less hazardous or non-hazardous materials;
  • Re-designing a component so that a hazardous material is not needed in its manufacture, use, or maintenance;
  • Changing a process to reduce or eliminate the hazardous material;
  • Extending shelf life; and
  • Restricting users.
Alternatives should be analyzed in a "could cost" approach, that is, considering the lowest cost by overcoming barriers to getting the job done, while ensuring protection of human health and the environment. In addition, alternatives that reduce water and/or energy consumption are also included in P2OAs because adverse environmental affects are typically associated with acquiring and providing these resources.

Compliance Site: Any regulated facility, regulated process, or a discharge to a regulated facility or process. Compliance sites include any location under Air Force control where the activity is subject to any current or future known requirements levied by federal, State, and local statutes and regulations; Executive Orders; Department of Defense (DoD) and Air Force policies; the Overseas Environmental Baseline Guidance Document (OEBGD), Final Governing Standards (FGS), and international agreements.

Cost Factor: The expense and the cost avoidance associated with a hazardous material that may be reduced to monetary terms, including future liability. Cost factors refer to direct and indirect costs attributable to HAZMATs that are encountered in any type of operation, such as acquisition, supply, engineering controls and disposal.

Economic Analysis: An evaluation of the costs associated with the use of HAZMAT and potential alternatives. Although several computer-based tools are available for completing an economic analysis, there is no single analysis process that will cover all situations. Economic analyses should be guided by the basic principles of economics and informed judgement.

Hazardous Materials Reduction Prioritization Process (HMRPP): The HMRPP provides a formalized way for installations to identify weapon system-driven HAZMAT reduction needs. This enables Major Command (MAJCOM) and installation priorities to drive weapon system HAZMAT reduction efforts. The weapon system HMRPP is not a separate requirements process. Rather, it integrates HAZMAT reduction requirements into the existing weapon system requirements, identification, prioritization, funding, and execution processes. Additional information on the HMRPP can be found in PRO-ACT's Air Force Weapon System HMRPP Fact Sheet.

Life Cycle Costs: An evaluation of the costs associated with the use of HAZMAT and potential alternatives over the life of the investment or the hazardous material. The analysis is not a specific step-by-step procedure, but must be guided by basic principles and informed judgement. Life cycle cost also incorporates the amortized annual cost of a product, including capital costs, installation, operating, maintenance and disposal costs discounted over the lifetime of the product.

Life Cycle of Hazardous Material: The period starting when the use or potential use of HAZMAT is first encountered, and extending as long as the actual material is in use, or its after effects (such as discarded residue in a landfill). In the case of weapons systems acquisition, the life cycle starts when the system is first envisioned. Effects of the use of HAZMAT on later operations and maintenance are also to be considered.

Mission Critical System: A system whose operational effectiveness and operations suitability are essential to successful completion. If this system fails, the mission will not be completed. Such a system can be auxiliary or supporting as well as a primary system.

Source reduction: Any practice that reduces the amount of a hazardous substance, pollutant, or contaminant entering the waste stream or otherwise released to the environment prior to recycling, treatment or disposal, and that reduces the hazards to public health and the environment. Source reduction may include, but is not limited to:

  • Equipment or technology modifications;
  • Process or procedure modifications;
  • Reformulation or redesign of products;
  • Substitution of raw materials; and
  • Improvements in housekeeping, maintenance, training or inventory control.
Source reduction considerations must be given the highest priority when researching and selecting P2 opportunity alternatives (see the Waste Management Hierarchy discussion below).

Waste Minimization: The reduction of the quantity or toxicity of a residual waste that is generated and subsequently processed, stored, or disposed. Its reduction minimizes present and future threats to human health and the environment.


Drivers for Conducting P2OAs
The need to conduct P2OAs is derived from AFI 32-7080; however, its roots are found in the Pollution Prevention Act and two Executive Orders that implement the provisions of the Act for federal agencies.

Pollution Prevention Act (PPA) [42 US Code . 13101, et seq.]. Congress passed the PPA in 1990 in order to establish a national policy whereby pollution should be prevented or reduced at the source rather than controlled after its production. The law requires specific action on the part of the Environmental Protection Agency (EPA) for setting up requirements in environmental protection programs, and the establishment of source reduction programs.

Executive Order (EO) 12856, Federal Compliance with Right-to-know-laws and Pollution Prevention Requirements, 6 August 1993. This EO requires the EPA administrator to promote source reduction in compliance with the PPA. It encourages companies to conduct their facility management and acquisition activities so that quantities of toxic chemicals entering any waste stream (including any release to the environment) are reduced as expeditiously as possible through source reduction. Further, the EO states that waste generated should be recycled to the maximum extent possible, and any remaining wastes are stored, treated or disposed of in a manner protective of public health and the environment. The federal government, the largest single consumer in the Nation, was targeted to lead the way in this endeavor. The EO proposes that the federal government should become a leader and set the example in the field of pollution prevention through the management of its facilities, its acquisition practices, and in supporting the development of innovative P2 programs and technologies.

Executive Order 13101, Greening the Government through Waste Prevention, Recycling, and Federal Acquisition, 14 September 1998. This EO serves to incorporate the concepts of waste prevention and recycling into daily operations, and to promote federal government preference and demand for environmentally preferable products, especially those containing recovered and recycled materials. Further, this EO reinforces the philosophy found in the PPA that if pollution cannot be prevented, it must be recycled, if not prevented or recycled, it must be treated in an environmentally safe manner. Disposal is viewed as the last resort.

"Pollution Prevention to Achieve Compliance," HQ USAF/ILEV Memorandum, 20 August 1997. This memorandum reemphasizes the Air Force's commitment to "compliance through pollution prevention" by stating that compliance requirements drive both traditional compliance (end of pipe treatment and disposal options) and pollution prevention. The memorandum also reaffirms that the environmental management hierarchy must be applied when developing solutions for every potential compliance requirement.

Air Force Policy Directive (AFPD) 32-70, Environmental Quality, 20 July 1994. This directive implements the provisions of the PPA and Executive Order 12856. In establishing the Air Force's Environmental Quality Program, it directly incorporates the PPA's charter of preventing future pollution by reducing the use of hazardous materials at the source.

Air Force Instruction 32-7080, Pollution Prevention, 12 May 1994. This AFI implements the pollution prevention portion of the Air Force Environmental Quality Program. Included within the AFI is a requirement for installations to conduct P2OAs on a recurring basis in order to assess all pollutant sources and determine opportunities for reducing or eliminating waste streams. P2OAs are to include all pollutant sources, examine total waste generation by type and volume, and determine the most economical and practical option for reduction. Results of the P2OAs are to be included in the installation's Pollution Prevention Management Action Plan (P2 MAP).

Draft Air Force Instruction 32-7080, Compliance Assurance and Pollution Prevention, undated. This update to the current AFI 32-7080, which is scheduled for release in 2000, specifies the use of the HMRPP for identifying and advocating changes to processes controlled by Technical Orders (T.O.s), and the use of process-specific P2OAs for processes not under T.O. control. It will require P2OA evaluations for a minimum of 4 percent of installation compliance sites each year beginning with the highest burden sites. As with the current version of AFI 32-7080, the draft requires installations to maintain a P2 MAP and to update it on an annual basis.

Air Force Instruction 32-7086, Hazardous Materials Management, 1 August 1997. Among its many provisions, this AFI establishes procedures and standards that govern the management of hazardous materials in the Air Force including the establishment of the Hazardous Materials Management Process (HMMP), and the creation of the HMRPP described above.


The Waste Management Hierarchy
The Pollution Prevention Act established a hierarchy for waste management that has been incorporated by the Air Force into its Environmental Quality Program. This hierarchy should be used in selecting potential pollution prevention opportunities and calls for:
  • Preventing or reducing pollution at the source whenever feasible;
  • Pollution that cannot be prevented should be recycled and/or reused in an environmentally safe manner;
  • Pollution that cannot be prevented or recycled should be treated in an environmentally safe manner whenever feasible; and
  • Disposal or other release into the environment should be employed only as a last resort and should be conducted in an environmentally safe manner.
At the top of the hierarchy is source reduction. As defined earlier in this fact sheet, source reduction means the elimination or reduction in the quantity or toxicity of wastes at their source of generation. In addition to being the most environmentally safe solution, source reduction techniques typically offer the best-cost advantages when compared to recycling, treatment, and disposal. More information on material/product substitutions can be found in PRO-ACT's Product Substitution Fact Sheet. Source reduction techniques include:
  • The most common source reduction technique is material substitution, where the current product is replaced with another product with less hazardous constituents.
  • Process efficiency improvements by which the same task is performed with less energy or materials through the modification of the existing process. There are several types of modifications that can be made to a process including the replacement or upgrading of existing equipment (e.g., replacing a solvent dip tank with an aqueous parts washer), and the changing or elimination of a step or steps in the process (e.g., eliminating a cleaning step prior to paint removal);
  • Better inventory control of hazardous materials to prevent the generation of expired or contaminated products that must then be disposed of as hazardous waste. Inventory control practices include purchasing materials in the proper unit of issue and maintaining only necessary quantities on hand, better distribution and tracking practices, reissuing partially used materials; and
  • Implementing better housekeeping practices and equipment preventive maintenance procedures to reduce the chances of spills and releases.
Recycling wastes after they have been generated is, as shown above, preferable to treatment or disposal. Some products (e.g., antifreeze, motor oil, and steel) and containers (e.g., 55-gallon drums, cardboard boxes, and plastic bottles) have fairly mature recycling markets that may return some funds to the installation. However, because the original product still had to purchased by the installation, the possible cost savings associated with recycling the waste will not be as large when compared against the prospect of reducing or eliminating the need to use the product. Another option closely related to recycling is reuse. Reuse is simply a means of extending the useful life of a chemical or material through multiple uses without processing (recycling requires that the material be treated or processed before it can be used again). An example of reuse would be taking used solvent that is generated from the final cleaning step in a multi-step process and reintroducing it earlier in the process where the need for using an ultra pure solvent is not necessary. Another, less elaborate example of reuse would involve collecting the packaging material from incoming shipments and then using this as packing material for outgoing shipments. Note: the reuse of some chemicals and materials could be considered unpermitted treatment or improper disposal of a hazardous waste under the Resource Conservation and Recovery Act (RCRA). PRO-ACT recommends that the reuse of any potentially hazardous material be coordinated on and approved by the installation's Environmental Management Flight.

Treatment and disposal of wastes are complex topics that are beyond the scope of this fact sheet. Readers are encouraged to discuss these "last resort" options with a representative from their installation Environmental Management Flight.


Conducting a P2OA
The pollution prevention opportunity assessment is an environmental analysis tool used to evaluate processes and operations. The goal of the assessment is to:
  • Identify and assess the amount of material disposed of as waste during a particular process or at a particular workplace;
  • Summarize hazardous materials usage and waste production;
  • Identify those operations needing improvement or replacement to accomplish pollution prevention; and
  • Establish a basis for prioritizing options developed during the assessment.
There are a variety of ways to conduct P2OAs. The stepped approach described below is presented as a "generic" example only, and is based upon guidance originally developed by the Headquarters Air Force Center for Environmental Excellence's Environmental Quality Directorate (HQ AFCEE/EQ) as part of their Pollution Prevention Opportunity Assessment Workshop. This process can be easily modified to meet installation-specific requirements. Additional guidance on conducting P2OAs has been incorporated into "shop-level," Internet-based pollution prevention training developed by HQ AFCEE/EQ and HQ AETC/LG-EM, in conjunction with HQ USAF/ILEV and P2 representatives from other MAJCOMs. Information on this resource is provided at the end of the fact sheet.

Step 1: Identify and Select the Process(es)

The first step in performing a P2OA is to select the process(es) you wish to evaluate. P2OAs can be performed at the installation and unit (e.g., squadron, shop, etc.) levels and encompass a large number of processes, or they can be focused down to a specific process. The best place to begin is with the highest priority process(es) based on command, regulatory, and environmental priorities (Note: the compliance site rankings required under the proposed update to AFI 32-7080 will encompass these priorities and thus help in the process selection). If there are several such sites, it may be best to begin with a process that generates a waste that is significantly more hazardous than other processes, or one that generates a higher quantity of waste than another. An important consideration in identifying and selecting processes is to be sure and keep the scope of the assessment at a manageable level. Trying to evaluate too many processes all at the same time can strain resources and reduce the overall quality of the assessment.

Step 2: Select the P2OA Team

Once the process(es) have been selected, it is time to build the assessment team. The team should consist of a variety of individuals with different backgrounds and skills, and ideally should contain a balanced mixture of personnel from the shop(s) responsible for the process(es) [including workers, supply staff, and supervisors], Environmental Management (EM), Bioenvironmental Engineering Services (BES), and the Hazardous Material Pharmacy (HAZMART). If multiple processes are being evaluated across several units, or even within the same shop, it may be beneficial to build a core team of personnel from EM, BES, and the HAZMART, and then supplement this core team with personnel from the shop responsible for each process. It is also quite useful to have someone on the team who is not an expert on the process, but who has successfully implemented some P2 options in their own shop. An important consideration in selecting the team is time. Conducting a P2OA on even one process can take a significant amount of effort once the time needed to collect the background information, identify alternatives, etc. is factored in. Team members need to have the commitment of their supervisors to see the assessment through to its completion. An alternative approach to building a P2OA team is to hire a responsible environmental consulting firm to conduct the assessment. This can be a successful and cost effective alternative, particularly when there is a need to assess processes across multiple units. Please remember that each shop will be required to devote time to answering questions regarding individual processes, even if an outside firm is hired.

Step 3: Examine the Process(es)

To examine the process it is important to characterize all aspects of the process or operation including sequencing of the steps in the process, waste generation patterns, material and energy consumption, costs, manpower, and reliance on hazardous/toxic chemicals. This can be accomplished by conducting site visits, interviewing shop staff, reviewing shop records, and collecting specific information concerning the process. Include visits to the shop storage areas, waste storage areas, and equipment areas. During this process, it is important to identify impacts that the process(es) and related wastes have on the air, water, and land. There can be a tendency to evaluate processes by first identifying the waste streams and then tracing them back to where they are introduced into the process. However, in doing this it is easy to miss materials that are consumed within the process including water and electricity. A better method is to start at the beginning of the process and then trace it step by step until its conclusion.

Prior to visiting the shop(s), it is important to gather the following information:

  • A listing of all hazardous materials issued to the shop during the past 12 months;
  • A copy of all hazardous waste turn in logs from the preceding 12 months;
  • Copies of all permits pertaining to the shop;
  • Listings of water and energy usage, solid waste disposal volumes/costs, and wastewater disposal volumes (if available);
  • An organizational chart and shop roster;
  • BEE process flow charts;
  • Previous P2OAs; and
  • Previous MAPs.
Often times shop personnel are unclear as to how much material is used and how much waste is generated in performing the tasks associated with a particular task, but their best guess is usually better and more accurate than computer data. Thus, the hazardous materials issues and hazardous waste turn in logs are extremely useful for characterizing the steps in the target process(es) because they are the most reliable measures of the inputs and outputs associated with performing the process tasks. Combining the information from these lists, along with knowledge of how often a particular process is performed and the composition of the hazardous materials, can lead to fairly accurate estimate of the inputs and outputs of the process each time it is performed. Water and energy usage logs, as well as solid waste disposal volumes/costs and wastewater disposal volumes may not be readily available unless individual buildings and/or shops on the installation are metered. Regardless, every effort should be made to quantify this information during the shop visit in order to conduct adequate cost/benefit analyses later in the P2OA process. Some of this information can be obtained from the shop itself; however, better sources often include records maintained by EM, BES, and the HAZMART.

Step 4: Establish a Baseline

All P2OAs require a baseline from which to conduct comparisons against potential alternatives. The first step in preparing the baseline is the creation of a process flow diagram. The diagram should describe the steps in the process, and identify all of the materials used and the wastes generated. The next step is to assign material and waste quantities to the diagram. These quantities must balance in the process; in other words, whatever goes into the process must come out either as part of a product or as a waste. It is also important to note in the diagram whether a Technical Order or Military Specification requires any of the materials used as this may limit potential alternatives.

Step 5: Identify Opportunities

This step in the assessment process can be the most difficult. Once everyone on the team has reviewed the process flow diagram, it is typical to have a "brainstorming session" in which the entire process is reviewed and ideas are solicited as to how the process could be changed. It is important at this stage not to discount any idea as being too outlandish; alternatives that are not truly feasible will eventually be removed from consideration. Once a list of potential opportunities has been prepared, research needs to be conducted to obtain information necessary to evaluate them and make final selections. There are a number of excellent resources available for finding information on potential opportunities. HQ AFCEE/EQ has prepared several P2OA Model Shop Reports pertinent to processes performed by Civil Engineering, aircraft maintenance organizations, pesticide management shops, and others. The Environmental Protection Agency (EPA) also has several helpful references that can be accessed from their World Wide Web (WWW) site at http://www.epa.gov/. The Defense Environmental Network and Information exchange (DENIX) is another helpful reference and is found at the WWW site http://www.denix.osd.mil/. PRO-ACT is also available to assist AF organizations with researching potential alternatives.

Step 6: Rank opportunities

The purpose in ranking opportunities is to see if they merit further consideration for implementation. The team needs to establish a standard set of criteria, based on the existing process, and against which it will evaluate the list of P2 opportunities. Selecting the criteria is an important task because they need to provide a consistent basis for justifying and funding future projects. Typical criteria include:

  • Cost;
  • Health and safety of the workers performing the process;
  • Environmental impact(s);
  • Changes in labor hours to perform the process;
  • Feasibility of implementing the opportunity; and
  • Impact on the unit's mission.
A decision matrix is then constructed in which each of the potential opportunities is scored against the standard criteria. Typically a scale of 1-10 is used with 10 being the most desirable, 1 being the least desirable, and 5 being neutral. For example, suppose a team is evaluating opportunities for degreasing metal parts. In the decision matrix shown below, procuring an aqueous parts washer may score high in the environmental impact and health categories because the cleaning solution is nontoxic, but low in the labor and mission impact categories because it takes longer to clean the parts and then dry them. Also, switching from one cleaner to another may score high in cost, but low in health and environmental impacts if it does not completely eliminate the necessity for personal protective equipment and still must be disposed of as a hazardous waste. It is important to remember that each opportunity is scored against the criteria, and hence against the current process, and not against one another. At the end of the scoring exercise, the total scores for each potential opportunity are determined, they are ranked from best to least, and a list of recommendations is prepared. Note: It may be necessary to perform a cost benefit analysis (CBA) on the opportunities in order to establish a payback period. The electronic versions of the P2OA Model Shop Reports mentioned above contain spreadsheets that can be used to conduct a CBA. They can be modified to incorporate many cost changes such as labor rates, disposal and purchase costs, and equipment purchase prices.
Post P2OA Activities
The P2OA team's work is essentially finished upon completion of the decision matrix and the ranking of the potential opportunities. From this point, the focus shifts primarily to those individuals responsible for advocating environmental initiatives. These individuals will take the recommendations from the team and develop the P2 MAP for implementing selected opportunities. Once the P2MAP has been developed, environmental program managers will need to seek funding for their projects. Readers are encouraged to review PRO-ACT's "Funding Air Force Environmental Projects" Fact Sheet for additional information and resources on this subject.


For More Information.
HQ AFCEE/EQ, in partnership with HQ AETC/LG-EM and other MAJCOM representatives, has developed the Shop Level Pollution Prevention Course. The course meets the training requirements in AFI 32-7086 and includes information on conducting P2OAs. The course is available on the WWW at http://www.afcee.brooks.af.mil/eq. Contact Ms. Tamee Tennison, HQ AFCEE/EQP, DSN 240-4670, Tamee.Tennison@hqafcee.brooks.af.mil, for assistance with the course or for assistance with other environmentally related training needs.

PRO-ACT can provide copies of HQ AFCEE/EQ's P2OA Model Shop Reports, as well as individual support to AF customers for researching potential opportunities. Contact PRO-ACT at DSN 240-4215, or submit research requests through the WWW at http://www.afcee.brooks.af.mil/pro_act/pro_acthome.asp.


References
  1. Pollution Prevention Act of 1990, 42 U.S.C. . 13101, et seq.
  2. EO 12856, Federal Compliance With Right-to-Know Laws and Pollution Prevention Requirements, 3 August 1993.
  3. EO 13101, Greening the Government through Waste Prevention, Recycling, and Federal Acquisition, 14 September 1998.
  4. Air Force Policy Directive (AFPD) 32-70, Environmental Quality, 20 July 1994
  5. Air Force Instruction 32-7086, Hazardous Materials Management, 1 August 1997
  6. Air Force Instruction 32-7080, Pollution Prevention, 12 May 1994
  7. Draft Air Force Instruction 32-7080, Compliance Assurance and Pollution Prevention, undated
  8. HQ AFCEE P2OA Model Shop Reports
  9. PRO-ACT Fact Sheet, Air Force Weapon System Hazardous Materials Reduction Prioritization Process (HMRPP), August 1999.
  10. PRO-ACT Fact Sheet, Product Substitution, November 1998
  11. PRO-ACT Fact Sheet, Funding Air Force Environmental Projects, October 1999
  12. EPA WWW site http://www.epa.gov/
  13. DENIX WWW site http://www.denix.osd.mil/