6.	COMMITMENTS AND CONTINGENCIES

Environmental Matters.

Regulatory Review of Perchlorates. Our Specialty Chemicals segment manufactures and sells products that contain perchlorates. Currently, perchlorate is on Contaminant Candidate List 3 of the U.S. Environmental Protection Agency (the “EPA”). In February 2011, the EPA announced that it had determined to move forward with the development of a regulation for perchlorates in drinking water, reversing its October 2008 preliminary determination not to promulgate such a regulation. Accordingly, the EPA announced its intention to begin to evaluate the feasibility and affordability of treatment technologies to remove perchlorate and to examine the costs and benefits of potential standards. The EPA has conducted various meetings, as required by the Safe Drinking Water Act, including a meeting of the Science Advisory Board, whose report has not yet been made public. We continue to monitor activities and expect the proposed regulation to be published in February 2013 followed by a 60-day public comment period. The earliest a final regulation is expected to be published is August 2014. Regulatory review and anticipated regulatory actions present general business risk to the Company, but no regulatory proposal of the EPA or any state in which we operate, to date, has been publicly announced that we believe would have a material effect on our results of operations and financial position or that would cause us to significantly modify or curtail our business practices, including our remediation activities discussed below.

Perchlorate Remediation Project in Henderson, Nevada. We commercially manufactured perchlorate chemicals at a facility in Henderson, Nevada (the “AMPAC Henderson Site”) from 1958 until the facility was destroyed in May 1988, after which we relocated our production to a new facility in Iron County, Utah. Kerr-McGee Chemical Corporation (“KMCC”) also operated a perchlorate production facility in Henderson, Nevada (the “KMCC Site”) from 1967 to 1998. In addition, between 1956 and 1967, American Potash operated a perchlorate production facility and, for many years prior to 1956, other entities also manufactured perchlorate chemicals at the KMCC Site. As a result of a longer production history in Henderson, KMCC and its predecessor operations manufactured significantly greater amounts of perchlorate over time than we did at the AMPAC Henderson Site.

In 1997, the Southern Nevada Water Authority (“SNWA”) detected trace amounts of the perchlorate anion in Lake Mead and the Las Vegas Wash. Lake Mead is a source of drinking water for Southern Nevada and areas of Southern California. The Las Vegas Wash flows into Lake Mead from the Las Vegas valley.

In response to this discovery by SNWA, and at the request of the Nevada Division of Environmental Protection (“NDEP”), we engaged in an investigation of groundwater near the AMPAC Henderson Site and down gradient toward the Las Vegas Wash. The investigation and related characterization, which lasted more than six years, employed experts in the field of hydrogeology. This investigation concluded that although there is perchlorate in the groundwater in the vicinity of the AMPAC Henderson Site up to 700 parts per million, perchlorate from this site does not materially impact, if at all, water flowing in the Las Vegas Wash toward Lake Mead. It has been well established, however, by data generated by SNWA and NDEP, that perchlorate from the KMCC Site did impact the Las Vegas Wash and Lake Mead. The Nevada Environmental Response Trust (“NERT”), which is the entity responsible for completing environmental remediation work at the Henderson location as a result of the 2010 settlement of the 2009 bankruptcy of KMCC’s successor, Tronox LLC, operates an above ground perchlorate groundwater remediation facility at their Henderson site. Tronox LLC is currently a tenant of NERT at the property.

Notwithstanding these facts, and at the direction of NDEP and the EPA, we conducted an investigation of remediation technologies for perchlorate in groundwater with the intention of remediating groundwater near the AMPAC Henderson Site. In 2002, we conducted a pilot test and in Fiscal 2005, we submitted a work plan to NDEP for the construction of a remediation facility near the AMPAC Henderson Site. The conditional approval of the work plan by NDEP in our third quarter of Fiscal 2005 allowed us to generate estimated costs for the installation and operation of the remediation facility to address perchlorate at the AMPAC Henderson Site. We commenced construction in July 2005. In December 2006, we began operations of the permanent facility. The location of this facility is several miles, in the direction of groundwater flow, from the AMPAC Henderson Site.

From time to time, we have held discussions with NDEP to formalize our remediation efforts in an agreement that, if executed, would provide more detailed regulatory guidance on environmental characterization and remedies at the AMPAC Henderson Site and vicinity. Typically, such agreements generally cover such matters as the scope of work plans, schedules, deliverables, remedies for non compliance, and reimbursement to the State of Nevada for past and future oversight costs. Discussions regarding a formal agreement are currently active and we anticipate that a formal agreement is likely to be completed during our Fiscal 2013.

Henderson Site Environmental Remediation Reserve. We accrue for anticipated costs associated with environmental remediation that are probable and estimable. On a quarterly basis, we review our estimates of future costs that could be incurred for remediation activities. In some cases, only a range of reasonably possible costs can be estimated. In establishing our reserves, the most probable estimate is used; otherwise, we accrue the minimum amount of the range.

During Fiscal 2005 and Fiscal 2006, we recorded aggregate charges of $26,000 representing our estimates at the time of the probable costs of our remediation efforts at the AMPAC Henderson Site, including the costs for capital equipment and on-going operating and maintenance (“O&M”).

Late in Fiscal 2009, we gained additional information from groundwater modeling that indicates groundwater emanating from the AMPAC Henderson Site in certain areas in deeper zones (more than 150 feet below ground surface) is moving toward our existing remediation facility at a much slower pace than previously estimated. Utilization of our existing facilities alone, at this slower groundwater pace, could, according to this groundwater model, extend the life of our remediation project to well in excess of fifty years. As a result of this additional data, related model interpretations and consultations with NDEP, we re-evaluated our remediation operations and determined that we should be able to improve the effectiveness of the treatment program and significantly reduce the total project time by expanding the treatment system existing at the time. The expansion includes installation of additional groundwater extraction wells in the deeper, more concentrated areas, construction of an underground pipeline to move extracted groundwater to our treatment facility, and the addition of fluidized bed reactor (“FBR”) bioremediation treatment equipment (the “Expansion Project”) that will enhance, and in some cases replace, primary components of the existing treatment system. In our Fiscal 2009 fourth quarter, we accrued $13,700 as our initial estimate of the capital cost of the Expansion Project and the related estimates of the effects of the enhanced operations on the on-going O&M costs and project life.

Through June 2011, and in cooperation with NDEP, we worked to develop the formal design, engineering and permitting of the Expansion Project. Based on data obtained through that date, which was largely comprised of firm quotations, we determined that significant modifications to our Fiscal 2009 assumptions were required. As a result, in June 2011, we accrued an additional $6,000 for the estimated increase in cost of the capital component of the Expansion Project, offset slightly by reductions in O&M cost estimates. The estimated capital costs of the Expansion Project increased by approximately $6,400. The increase reflected (i) an increase in the capacity of the FBR bioremediation treatment equipment to accommodate technical requirements based on the testing of new extraction wells in the fall of 2010, and (ii) higher than initially anticipated cost associated with the installation of the equipment and construction of the pipeline. Our estimate of total O&M costs was reduced by approximately $400.

In September 2012, we commenced initial operation of the Expansion Project. Related system optimization and other start-up activities will continue into Fiscal 2013. In September 2012, we recorded an additional remediation charge in the amount of $700, which is substantially attributed to the true-up of estimates to the expected final cost of the Expansion Project. Due to uncertainties inherent in making estimates, our estimates of capital and O&M costs may later require significant revision as new facts become available and circumstances change.

The estimated life of the project is a key assumption underlying the accrued estimated cost of our remediation activities. Groundwater modeling and other information regarding the characteristics of the surrounding land and demographics indicate that at our targeted processing rate of 450 gallons per minute for the new groundwater extraction wells (750 gallons per minute in the aggregate with existing wells), the life of the project could range from 5 to 18 years from the date that the Expansion Project was placed in service. Further, the data indicates that within that range, 7 to 14 years is the more likely range. In accordance with generally accepted accounting principles, if no point within the more likely range is considered more likely than another, then estimates should be based on the low end of the range. Accordingly, our accrued remediation cost includes estimated O&M costs through 2019, which is the low end of the likely range of the project life. Groundwater speed, perchlorate concentrations, aquifer characteristics and forecasted groundwater extraction rates will continue to be key factors considered when estimating the life of the project. If additional information becomes available in the future that leads to a different interpretation of the model, thereby dictating a change in equipment and operations, our estimate of the resulting project life could change significantly.

The estimate of the annual O&M cost of the project is a key assumption in our computation of the estimated cost of our remediation activities. To estimate O&M costs, we consider, among other factors, the project scope and historical expense rates to develop assumptions regarding labor, utilities, repairs, maintenance supplies and professional services costs. We estimate average annual O&M costs to be approximately $1,900. If additional information becomes available in the future that is different than information currently available to us and thereby leads us to different conclusions, our estimate of O&M expenses could change significantly.

In addition, certain remediation activities are conducted on public lands under operating permits. In general, these permits may require us to relocate our underground pipeline or equipment to accommodate future public utilities and features and require us to return the land to its original condition at the end of the permit period. If we are required to relocate our underground pipeline or equipment in the future, the costs of such activities would be incremental to our current cost estimates. Estimated costs associated with removal of remediation equipment from the land are not material and are included in our range of estimated costs.

As of December 31, 2012, the aggregate range of anticipated environmental remediation costs was from approximately $10,900 to approximately $34,800. This range represents a significant estimate and is based on the estimable elements of cost for capital and O&M costs, and an estimated remaining operating life of the project through a range from the years 2017 to 2030. As of December 31, 2012, the accrued amount was $14,666, based on an estimated remaining life of the project through the year 2019, or the low end of the more likely range of the expected life of the project. Cost estimates are based on our current assessments of the facility configuration. As we proceed with the project, we have, and may in the future, become aware of elements of the facility configuration that must be changed to meet the targeted operational requirements. Certain of these changes may result in corresponding cost increases. Costs associated with the changes are accrued when a reasonable alternative, or range of alternatives, is identified and the cost of such alternative is estimable. Our estimated reserve for environmental remediation is based on information currently available to us and may be subject to material adjustment upward or downward in future periods as new facts or circumstances may indicate.

A summary of our environmental reserve activity for the three months ended December 31, 2012 is shown below:


Balance, September 30, 2012	$	16,754
Expenditures		(2,088)

Balance, December 31, 2012	$	14,666

AFC Environmental Matters. The primary operations of our Fine Chemicals segment are located on land leased from Aerojet-General Corporation (“Aerojet”), a wholly-owned subsidiary of GenCorp Inc. (“GenCorp”). The leased land is part of a tract of land owned by Aerojet designated as a “Superfund site” under the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (“CERCLA”). The tract of land had been used by Aerojet and affiliated companies to manufacture and test rockets and related equipment since the 1950s. Although the chemicals identified as contaminants on the leased land were not used by Aerojet Fine Chemicals LLC (predecessor in interest to Ampac Fine Chemicals LLC) as part of its operations, CERCLA, among other things, provides for joint and several liability for environmental liabilities including, for example, environmental remediation expenses.

As part of the agreement by which we acquired our Fine Chemicals segment business from GenCorp, an Environmental Indemnity Agreement was entered into whereby GenCorp agreed to indemnify us against any and all environmental costs and liabilities arising out of or resulting from any violation of environmental law prior to the effective date of the sale, or any release of hazardous substances by Aerojet Fine Chemicals LLC, Aerojet or GenCorp on the premises of Ampac Fine Chemicals LLC or Aerojet’s Sacramento site prior to the effective date of the sale.

On November 29, 2005, EPA Region IX provided us with a letter indicating that the EPA does not intend to pursue any clean up or enforcement actions under CERCLA against future lessees of the Aerojet property for existing contamination, provided that the lessees do not contribute to or do not exacerbate existing contamination on or under the Aerojet Superfund site.

Other Matters. Although we are not currently party to any material pending legal proceedings, we are from time to time subject to claims and lawsuits related to our business operations. We accrue for loss contingencies when a loss is probable and the amount can be reasonably estimated. Legal fees, which can be material in any given period, are expensed as incurred. We believe that current claims or lawsuits against us, individually and in the aggregate, will not result in loss contingencies that will have a material adverse effect on our financial condition, cash flows or results of operations.