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| 1 | CONSOLIDATED EDISON INC | Note G—Environmental Matters Superfund Sites Hazardous substances, such as asbestos, polychlorinated biphenyls (PCBs) and coal tar, have been used or generated in the course of operations of the Utilities and their predecessors and are present at sites and in facilities and equipment they currently or previously owned, including sites at which gas was manufactured or stored.
The Federal Comprehensive Environmental Response, Compensation and Liability Act of 1980 and similar state statutes (Superfund) impose joint and several liability, regardless of fault, upon generators of hazardous substances for investigation and remediation costs (which include costs of demolition, removal, disposal, storage, replacement, containment, and monitoring) and environmental damages. Liability under these laws can be material and may be imposed for contamination from past acts, even though such past acts may have been lawful at the time they occurred. The sites at which the Utilities have been asserted to have liability under these laws, including their manufactured gas plant sites and any neighboring areas to which contamination may have migrated, are referred to herein as “Superfund Sites.”
For Superfund Sites where there are other potentially responsible parties and the Utilities are not managing the site investigation and remediation, the accrued liability represents an estimate of the amount the Utilities will need to pay to discharge their related obligations. For Superfund Sites (including the manufactured gas plant sites) for which one of the Utilities is managing the investigation and remediation, the accrued liability represents an estimate of the company’s share of undiscounted cost to investigate the sites and, for sites that have been investigated in whole or in part, the cost to remediate the sites. Remediation costs are estimated in light of the information available, applicable remediation standards, and experience with similar sites.
The accrued liabilities and regulatory assets related to Superfund Sites at September 30, 2009 and December 31, 2008 were as follows:
Most of the accrued Superfund Site liability relates to sites that have been investigated, in whole or in part. As investigations progress on these and other sites, the Utilities expect that additional liability will be accrued, the amount of which is not presently determinable but may be material. Under their current rate agreements, the Utilities are permitted to recover or defer as regulatory assets (for subsequent recovery through rates) certain site investigation and remediation costs.
Environmental remediation costs incurred related to Superfund Sites during the three and nine months ended September 30, 2009 and 2008 were as follows:
In 2006, Con Edison of New York estimated that for its manufactured gas plant sites, its aggregate undiscounted potential liability for the investigation and remediation of coal tar and/or other manufactured gas plant-related environmental contaminants could range up to $1.1 billion. In 2007, O&R estimated that for its manufactured gas plant sites, each of which has been investigated, the aggregate undiscounted potential liability for the remediation of such contaminants could range up to $115 million. These estimates were based on the assumption that there is contamination at the sites that have not yet been investigated and additional assumptions about these and the other sites regarding the extent of contamination and the type and extent of remediation that may be required. Actual experience may be materially different.
Asbestos Proceedings Suits have been brought in New York State and federal courts against the Utilities and many other defendants, wherein a large number of plaintiffs sought large amounts of compensatory and punitive damages for deaths and injuries allegedly caused by exposure to asbestos at various premises of the Utilities. The suits that have been resolved, which are many, have been resolved without any payment by the Utilities, or for amounts that were not, in the aggregate, material to them. The amounts specified in all the remaining thousands of suits total billions of dollars; however, the Utilities believe that these amounts are greatly exaggerated, based on the disposition of previous claims. In 2008, Con Edison of New York estimated that its aggregate undiscounted potential liability for these suits and additional suits that may be brought over the next 15 years is $9 million. The estimate was based upon a combination of modeling, historical data analysis and risk factor assessment. Actual experience may be materially different. In addition, certain current and former employees have claimed or are claiming workers’ compensation benefits based on alleged disability from exposure to asbestos. Under its current rate agreements, Con Edison of New York is permitted to defer as regulatory assets (for subsequent recovery through rates) costs incurred for its asbestos lawsuits and workers’ compensation claims. The accrued liability for asbestos suits and workers’ compensation proceedings (including those related to asbestos exposure) and the amounts deferred as regulatory assets for the Companies at September 30, 2009 and December 31, 2008 were as follows:
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| 2 | CONSTELLATION ENERGY GROUP INC |
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| 3 | FMC Corporation | Note 13: Environmental Obligations
We have provided reserves for potential environmental obligations, which management considers probable and for which a reasonable estimate of the obligation could be made. Accordingly, reserves of $182.7 million and $194.2 million, excluding recoveries, have been provided at September 30, 2009 and December 31, 2008, respectively.
At September 30, 2009 and December 31, 2008, expected recoveries were $58.1 million and $47.7 million, respectively, relating to existing contractual arrangements with U.S. government agencies, insurance carriers and other third parties. Recoveries are recorded as either an offset to the “Environmental liabilities, continuing and discontinued” balance totaling $19.0 million and $21.5 million at September 30, 2009 and December 31, 2008, respectively, or as “Other assets” totaling $39.1 million and $26.2 million at both September 30, 2009 and December 31, 2008, respectively, in the condensed consolidated balance sheets. Cash recoveries recorded as realized claims against third parties were $6.8 million in the first nine months of 2009. Total cash recoveries recorded for the year ended December 31, 2008 were $5.6 million.
The long-term portion of environmental reserves, net of recoveries, totaling $150.5 million and $158.8 million at September 30, 2009 and December 31, 2008, respectively, is included in “Environmental liabilities, continuing and discontinued”. The short-term portion of continuing obligations is recorded as “Accrued and other liabilities”.
We have estimated that reasonably possible environmental loss contingencies may exceed amounts accrued by approximately $80 million at September 30, 2009. Obligations that have not been reserved for may be material to any one quarter’s or year’s results of operations in the future. However, we believe any such liability arising from potential environmental obligations is not likely to have a materially adverse effect on our liquidity or financial condition and may be satisfied over the next twenty years or longer.
The table below is a rollforward of our environmental reserves, continuing and discontinued, from December 31, 2008 to September 30, 2009:
(1) “Current” includes only those reserves related to continuing operations. A more complete description of our environmental contingencies and the nature of our potential obligations are included in Notes 1 and 12 to our 2008 consolidated financial statements in our 2008 Form 10-K. |
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| 4 | FORTUNE BRANDS INC |
We are subject to laws and regulations relating to the protection of the environment. It is not possible to quantify with certainty the potential impact of actions relating to environmental matters, particularly remediation and other compliance efforts that our subsidiaries may undertake in the future. In our opinion, however, compliance with current environmental protection laws (before taking into account estimated recoveries from third parties) will not have a material adverse effect upon our results of operations, cash flows or financial condition. |
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| 5 | NRG ENERGY, INC. |
Note 17 — Environmental Matters
The construction and operation of power projects are subject to stringent environmental and
safety protection and land use laws and regulation in the United States. If such laws and
regulations become more stringent, or new laws, interpretations or compliance policies apply and
NRG’s facilities are not exempt from coverage, the Company could be required to make modifications
to further reduce potential environmental impacts. New legislation and regulations to mitigate the
effects of greenhouse gases, or GHGs, including CO2 from power plants, are under
consideration at the federal and state levels. In general, the effect of such future laws or
regulations is expected to require the addition of pollution control equipment or the imposition of
restrictions or additional costs on the Company’s operations.
Environmental Capital Expenditures
Based on current rules, technology and plans, NRG has estimated that environmental capital
expenditures from 2010 through 2013 to meet NRG’s environmental commitments will be approximately
$900 million and are primarily associated with controls on the Company’s Big Cajun and Indian River
facilities. These capital expenditures, in general, are related to installation of particulate,
SO2, NOx, and mercury controls to comply with federal and state air quality
rules and consent orders, as well as installation of “Best Technology Available” under the Phase II
316(b) Rule. NRG continues to explore cost effective alternatives that can achieve desired
results. This estimate reflects anticipated schedules and controls related to the Clean Air
Interstate Rule, or CAIR, Maximum Achievable Control Technology, or MACT, for mercury, and the
Phase II 316(b) Rule which are under remand to the U.S. EPA, and, as such, the full impact on the
scope and timing of environmental retrofits from any new or revised regulations cannot be
determined at this time.
Northeast Region
NRG operates electric generating units located in Connecticut, Delaware, Maryland,
Massachusetts and New York which are subject to RGGI. These units must surrender one allowance for
every U.S. ton of CO2 emitted with true up for 2009-2011 occurring in 2012. Allowances
are partially allocated only in the state of Delaware. In 2008, NRG emitted approximately 12
million tonnes of CO2 in RGGI states, although 2009 is tracking lower than 2008 year to
date. NRG believes that to the extent CO2 will not be fully reflected in wholesale
electricity prices, the direct financial impact on the Company is likely to be negative as costs
will be incurred in the course of securing the necessary RGGI allowances and offsets at auction and
in the market.
In January 2006, NRG’s Indian River Operations, Inc. received a letter of informal
notification from the DNREC stating that the Company may be a potentially responsible party with
respect to a historic captive landfill. On October 1, 2007, NRG signed an agreement with the DNREC
to investigate the site through the Voluntary Clean-up Program. On February 4, 2008, the DNREC
issued findings that no further action is required in relation to surface water and that a
previously planned shoreline stabilization project would adequately address shoreline erosion. The
landfill itself will require a further Remedial Investigation and Feasibility Study to determine
the type and scope of any additional work required. Until the Remedial Investigation and
Feasibility Study is completed, the Company is unable to predict the impact of any required
remediation.
On May 29, 2008, the DNREC requested that NRG’s Indian River Operations, Inc. participate in
the development and performance of a Natural Resource Damage Assessment, or NRDA, at the Burton
Island Old Ash Landfill. NRG is currently working with the DNREC and other trustees to close out
the assessment phase.
South Central Region
On February 11, 2009, the U.S. Department of Justice acting at the request of the U.S. EPA
commenced a lawsuit against Louisiana Generating, LLC in federal district court in the Middle
District of Louisiana alleging violations of the CAA at the Big Cajun II power plant. This is the
same matter for which NOVs were issued to Louisiana Generating, LLC on February 15, 2005, and on
December 8, 2006. Further discussion on this matter can be found in Note 15, Commitments and
Contingencies, to this Form 10-Q, Louisiana Generating, LLC.
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| 6 | OCCIDENTAL PETROLEUM CORP /DE/ |
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| 7 | PROGRESS ENERGY INC |
We are subject to regulation by various federal, state and local authorities in the areas of air quality, water quality, control of toxic substances and hazardous and solid wastes, and other environmental matters. We believe that we are in substantial compliance with those environmental regulations currently applicable to our business and operations and believe we have all necessary permits to conduct such operations. Environmental laws and regulations frequently change and the ultimate costs of compliance cannot always be precisely estimated.
The provisions of the Comprehensive Environmental Response, Compensation and Liability Act of 1980, as amended (CERCLA), authorize the EPA to require the cleanup of hazardous waste sites. This statute imposes retroactive joint and several liability. Some states, including North Carolina, South Carolina and Florida, have 55 similar types of statutes. We are periodically notified by regulators, including the EPA and various state agencies, of our involvement or potential involvement in sites that may require investigation and/or remediation. There are presently several sites with respect to which we have been notified of our potential liability by the EPA, the state of North Carolina, the state of Florida, or potentially responsible party (PRP) groups as described below in greater detail. Various organic materials associated with the production of manufactured gas, generally referred to as coal tar, are regulated under federal and state laws. PEC and PEF are each PRPs at several manufactured gas plant (MGP) sites. We are also currently in the process of assessing potential costs and exposures at other sites. These costs are eligible for regulatory recovery through either base rates or cost-recovery clauses. Both PEC and PEF evaluate potential claims against other PRPs and insurance carriers and plan to submit claims for cost recovery where appropriate. The outcome of potential and pending claims cannot be predicted. A discussion of sites by legal entity follows. We record accruals for probable and estimable costs related to environmental sites on an undiscounted basis. We measure our liability for these sites based on available evidence including our experience in investigating and remediating environmentally impaired sites. The process often involves assessing and developing cost-sharing arrangements with other PRPs. For all sites, as assessments are developed and analyzed, we will accrue costs for the sites to the extent our liability is probable and the costs can be reasonably estimated. Because the extent of environmental impact, allocation among PRPs for all sites, remediation alternatives (which could involve either minimal or significant efforts), and concurrence of the regulatory authorities have not yet reached the stage where a reasonable estimate of the remediation costs can be made, we cannot determine the total costs that may be incurred in connection with the remediation of all sites at this time. It is probable that current estimates will change and additional losses, which could be material, may be incurred in the future. The following table contains information about accruals for probable and estimable costs related to various environmental sites, which were included in other current liabilities and other liabilities and deferred credits on the Balance Sheets:
PROGRESS ENERGY In addition to the Utilities’ sites, discussed under “PEC” and “PEF” below, we incurred indemnity obligations related to certain pre-closing liabilities of divested subsidiaries, including certain environmental matters (See discussion under Guarantees in Note 16B). PEC Including the Ward Transformer site located in Raleigh, N.C. (Ward), and MGP sites discussed below, for the three months ended September 30, 2009, PEC reduced its accrual by approximately $1 million and spent approximately $2 million. For the nine months ended September 30, 2009, PEC accrued approximately $3 million and spent approximately $6 million. For the three months ended September 30, 2008, PEC accrued approximately $2 million and spent approximately $2 million. For the nine months ended September 30, 2008, PEC accrued approximately $8 million and spent approximately $6 million. These amounts primarily relate to the Ward site. PEC has recorded a minimum estimated total remediation cost for all of its remaining MGP sites based upon its historical experience with remediation of several of its MGP sites. The maximum amount of the range for all the sites cannot be determined at this time as one of the remaining sites is significantly larger than the sites for which we 56 have historical experience. Actual experience may differ from current estimates, and it is probable that estimates will continue to change in the future. In 2004, the EPA advised PEC that it had been identified as a PRP at the Ward site. The EPA offered PEC and a number of other PRPs the opportunity to negotiate the removal action for the Ward site and reimbursement to the EPA for the EPA’s past expenditures in addressing conditions at the Ward site. Subsequently, PEC and other PRPs signed a settlement agreement, which requires the participating PRPs to remediate the Ward site. At September 30, 2009 and December 31, 2008, PEC’s recorded liability for the site was approximately $4 million and $7 million, respectively. Actual experience may differ from current estimates, and it is probable that estimates will continue to change in the future. On September 12, 2008, PEC filed an initial civil action against a number of PRPs seeking contribution for and recovery of costs incurred in remediating the Ward site, as well as a declaratory judgment that defendants are jointly and severally liable for response costs at the site. On March 13, 2009, a subsequent action was filed against additional PRPs, and on April 30, 2009, suit was filed against the remaining approximately 160 PRPs. PEC has settled with a number of the PRPs and is in active settlement negotiations with others. With respect to the defendants that do not settle, the federal district court in which this matter is pending requires that alternative dispute resolution be pursued early in civil litigation but it is unclear what process the court will require. The outcome of these matters cannot be predicted. On September 30, 2008, the EPA issued a Record of Decision for the operable unit for stream segments downstream from the Ward site (Ward OU1) and advised 61 parties, including PEC, of their identification as PRPs for Ward OU1 and for the operable unit for further investigation at the Ward facility and certain adjacent areas (Ward OU2). The EPA’s estimate for the selected remedy for Ward OU1 is approximately $6 million. The EPA offered PEC and the other PRPs the opportunity to negotiate implementation of a response action for Ward OU1 and a remedial investigation and feasibility study for Ward OU2, as well as reimbursement to the EPA of approximately $1 million for the EPA’s past expenditures in addressing conditions at the site. On January 19, 2009, PEC and several of the other participating PRPs at the Ward site submitted a letter containing a good faith response to the EPA’s special notice letter. Another group of PRPs separately submitted a good faith response, which the EPA advised would be used to negotiate implementation of the required actions. The other PRPs’ good faith response was subsequently withdrawn. Discussions among representatives of certain PRPs, including PEC, and the EPA are ongoing. Although a loss is considered probable, an agreement among the PRPs for these matters has not been reached; consequently, it is not possible at this time to reasonably estimate the total amount of PEC’s obligation, if any, for Ward OU1 and Ward OU2. PEF PEF has received approval from the FPSC for recovery through the environmental cost recovery clause (ECRC) of the majority of costs associated with the remediation of distribution and substation transformers. Under agreements with the Florida Department of Environmental Protection (FDEP), PEF has reviewed all distribution transformer sites and all substation sites for mineral oil-impacted soil caused by equipment integrity issues. Should further distribution transformer sites be identified outside of this population, the distribution O&M costs will not be recoverable through the ECRC. For the three and nine months ended September 30, 2009, PEF accrued approximately $9 million and $11 million, respectively, due to the identification of additional transformer sites and an increase in estimated remediation costs, and spent approximately $4 million and $11 million, respectively, related to the remediation of transformers. For the three and nine months ended September 30, 2008, PEF accrued approximately $3 million and $15 million, respectively, due to the identification of additional transformer sites and an increase in estimated remediation costs, and spent approximately $6 million and $20 million, respectively, related to the remediation of transformers. At September 30, 2009, PEF had recorded a regulatory asset for the probable recovery of costs through the ECRC related to the sites included under the agreement with the FDEP. The accruals for MGP and other sites, in the previous table, relate to two former MGP sites and other sites associated with PEF that have required, or are anticipated to require, investigation and/or remediation. For the three months ended September 30, 2009, PEF made no material accruals or expenditures. For the nine months ended September 30, 2009, PEF made no material accruals and spent approximately $2 million, which primarily related to its MGP sites. For the three and nine months ended September 30, 2008, PEF made no material accruals or expenditures. 57
At September 30, 2009 and December 31, 2008, we were subject to various current federal, state and local environmental compliance laws and regulations governing air and water quality, resulting in capital expenditures and increased O&M expenses. These compliance laws and regulations included the Clean Air Interstate Rule (CAIR), the Clean Air Visibility Rule (CAVR), the North Carolina Clean Smokestacks Act, enacted in June 2002 (Clean Smokestacks Act) and mercury regulation. PEC’s and PEF’s environmental compliance capital expenditures related to these regulations began in 2002 and 2005, respectively. Through September 30, 2009, cumulative environmental compliance capital expenditures since 2002 with regard to these environmental laws and regulations were $2.084 billion, including $1.051 billion at PEC and $1.033 billion at PEF. Through December 31, 2008, cumulative environmental compliance capital expenditures to date with regard to these environmental laws and regulations were $1.859 billion, including $1.012 billion at PEC, which primarily relates to Clean Smokestacks Act projects, and $847 million at PEF. PEF participated in a coalition of Florida utilities that filed a challenge to the CAIR as it applied to Florida. PEF withdrew from the coalition during the fourth quarter of 2008. On July 11, 2008, the U.S. Court of Appeals for the District of Columbia (D.C. Court of Appeals) issued its decision on multiple challenges to the CAIR, including the Florida challenge, which vacated the CAIR in its entirety. On September 24, 2008, petitions for rehearing were filed by a number of parties. On December 23, 2008, the D.C. Court of Appeals remanded the CAIR without vacating the rule for the EPA to conduct further proceedings consistent with the D.C. Court of Appeals’ prior opinion. The outcome of the EPA’s further proceedings cannot be predicted. Because the D.C. Court of Appeals’ December 23, 2008 decision remanded the CAIR, the current implementation of the CAIR continues to fulfill best available retrofit technology (BART) for SO2 and nitrogen oxides (NOx) for BART-affected units under the CAVR. Should this determination change as the CAIR is revised, CAVR compliance eventually may require consideration of NOx and SO2 emissions in addition to particulate matter emissions for BART-eligible units. On February 8, 2008, the D.C. Court of Appeals vacated the delisting determination and the Clean Air Mercury Rule (CAMR). The three states in which the Utilities operate adopted mercury regulations implementing CAMR and submitted their state implementation rules to the EPA. It is uncertain how the decision that vacated the federal CAMR will affect the state rules; however, state-specific provisions are likely to remain in effect. The North Carolina mercury rule contains a requirement that all coal-fired units in the state install mercury controls by December 31, 2017, and requires compliance plan applications to be submitted in 2013. We are currently evaluating the impact of these decisions. The outcome of these matters cannot be predicted. PEF is continuing construction of its in-process emission control projects. On December 18, 2008, PEF and the FDEP announced an agreement under which PEF will retire Crystal River Units No. 1 and No. 2 (CR1 and CR2) as coal-fired units and complete construction of its emission control projects at CR4 and CR5. CR1 and CR2 will be retired after the second proposed nuclear unit at Levy completes its first fuel cycle, which was anticipated to be around 2020. On May, 1, 2009, PEF announced that it expects the construction schedule to shift later than the originally estimated 2016 to 2018 timeframe by a minimum of 20 months for the commercial operation dates of Levy. We are currently evaluating the impacts of the schedule shift. We cannot predict the outcome of this matter. We account for emission allowances as inventory using the average cost method. We value inventory of the Utilities at historical cost consistent with ratemaking treatment. The EPA is continuing to record allowance allocations under the CAIR NOx trading program, in some cases for years beyond the estimated two-year period for promulgation of a replacement rule. The EPA’s continued recording of CAIR NOx allowance allocations does not guarantee that allowances will continue to be usable for compliance after a replacement rule is finalized or that they will continue to have value in the future. SO2 emission allowances will be utilized to comply with existing Clean Air Act requirements. PEF’s CAIR expenses, including NOx allowance inventory expense, are recoverable through the ECRC. At September 30, 2009 and December 31, 2008, PEC had approximately $15 million and $22 million, respectively, in SO2 emission allowances and an immaterial amount of NOx emission allowances. At September 30, 2009 and December 31, 2008, PEF had approximately $8 million and $11 million, respectively, in SO2 emission allowances and approximately $43 million and $65 million, respectively, in NOx emission allowances. In June 2002, the Clean Smokestacks Act was enacted in North Carolina requiring the state's electric utilities to reduce the emissions of NOx and SO2 from their North Carolina coal-fired power plants in phases by 2013. Two of PEC’s largest coal-fired generating units (the Roxboro No. 4 and Mayo Units) impacted by the Clean Smokestacks Act are jointly owned. Pursuant to joint ownership agreements, the joint owners are required to pay a portion of the 58 costs of owning and operating these plants. PEC has determined that the most cost-effective Clean Smokestacks Act compliance strategy is to maximize the SO2 removal from its larger coal-fired units, including Roxboro No. 4 and Mayo, so as to avoid the installation of expensive emission controls on its smaller coal-fired units. In order to address the joint owner's concerns that such a compliance strategy would result in a disproportionate share of the cost of compliance for the jointly owned units, in 2005 PEC entered into an agreement with the joint owner to limit its aggregate costs associated with capital expenditures to comply with the Clean Smokestacks Act to approximately $38 million. PEC recorded a related liability for the joint owner's share of estimated costs in excess of the contract amount. The terms of the agreement place no limit on PEC’s maximum remaining liability; however, PEC estimates its remaining exposure to be $2 million at September 30, 2009. At September 30, 2009 and December 31, 2008, the amount of the liability was $2 million and $10 million, respectively, based upon the respective estimates for the remaining Clean Smokestacks Act compliance costs. During the three months ended September 30, 2009, PEC made no additional accruals and spent approximately $5 million that exceeded the joint owner limit. During the nine months ended September 30, 2009, PEC accrued approximately $2 million and spent approximately $10 million that exceeded the joint owner limit (See Note 16B). Because PEC has taken a system-wide compliance approach, its North Carolina retail ratepayers have significantly benefited from the strategy of focusing emission reduction efforts on the jointly owned units, and, therefore, PEC believes that any costs in excess of the joint owner’s share should be recovered from North Carolina retail ratepayers, consistent with other capital expenditures associated with PEC’s compliance with the Clean Smokestacks Act. On September 5, 2008, the NCUC ordered that PEC shall be allowed to include in rate base all reasonable and prudently incurred environmental compliance costs in excess of $584 million, including eligible compliance costs in excess of the joint owner’s share, as the projects are closed to plant in service. |
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