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Watersbend: appraising a brownfield redevelopment project. (Features).

Abstract

This paper examines issues affecting the appraisal of a brownfield apartment property in Austin, Texas. These issues include the contamination that forced the property's evacuation, its eventual remediation, the creation of the legal framework permitting its reoccupation, market acceptance of its safety, and ongoing stigma risks. The authors describe the research and methodology needed to quantify the risks of owning a brownfield property. They conclude that complicated and long-term redevelopment projects such as this one can be successfully and profitably redeveloped while suffering only a modest post-remediation stigma.

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One of the most notorious events in the real estate history of Austin, Texas, took place in 1991 when approximately 1,000 tenants were forced to evacuate on forty-eight hours notice from the Watersbend apartment complex. State environmental officials had discovered that potentially explosive levels of methane had seeped into ground-floor units overlaying a former municipal landfill. Eight years passed before the property accepted new tenants. During that time, the property was looted, new legislation was enacted to facilitate its remediation, and millions were spent on its rehabilitation.

Watersbend is one of the most unusual but ultimately successful brownfield redevelopment cases in Texas. This property was appraised just prior to its reopening, and the appraisal required research of the property's history, laws that expedited its remediation, the potential for tenant resistance, and environmental risks that could affect its value. This article discusses the complete history of the property: the bizarre circumstances of its construction, evacuation, and abandonment; its lengthy and groundbreaking remediation project; the recently enacted laws that permitted its rehabilitation; its reopening and market acceptance; and the multiple risks affecting its value then, now, and into the future. The authors believe the property suffers from a small but definite residual stigma, but on the whole its redevelopment is a resounding success that could serve as a model for other brownfield sites.

The impact of contamination on real estate is established in several articles. In 1991, Peter Patchin, MAI, in "Contaminated Properties Stigma Revisited," noted the development of data proving the existence of stigma in contaminated properties. (1) Patchin described stigma as a "negative intangible" caused by fear of hidden cleanup costs and public liability, lack of mortgageability, and the trouble factor, defined as monetary compensation for going to the "trouble of making a necessary improvement to a contaminated property.

In 1992, Bill Mundy, MAI, PhD, discussed how contamination affects property value over time in his article "The Impact of Hazardous Materials on Property Value." (2) He maintains that property damages are manifested in lost income, utility, and marketability. In the early stage when uncertainty is highest, loss in value is greatest as a result of loss in marketability caused by "disclosure requirement by the sales agent or seller, required disclosure statements, concern on the part of the lender, and appraiser uncertainty." Damages decrease as the situation is understood and uncertainty is lessened. Mundy also describes residual stigma as "the difference between cured value and full market value," noting that cured value may never reach unimpaired value because of public perception of health risks.

A more recent article, "Post-Repair Diminution in Value from Geotechnical Problems" by Michael V. Sanders addresses the case studies approach and its applicability to estimating damages to properties affected by contamination and construction defects. (3) Sanders states that "the measurement of residual loss in value or stigma best employs the use of case studies." He further states that "case study properties need not be in the same area as the subject property, and data limitations usually necessitate searching a broader geographical area. While the circumstances surrounding the loss in value may be similar, properties selected for case studies are in many cases not directly comparable to the subject."

Robert Simons, PhD, discusses brownfields and their redevelopment in several articles and books listed in the bibliography. In his book Turning Brownfields into Greenbacks, Simons notes that the primary obstacles to brownfield redevelopment are the cost of cleanup and liability. (4) Regarding the cost of cleanup, he describes a relatively common situation in which the "net price of urban land [the cost of purchasing and remediating the land] possibly contaminated by a prior use would be higher than a comparable suburban property on virgin farmland." He also notes that the "strict, joint, and several liability" clauses of the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) and Superfund Amendments and Reauthorization Act (SARA) have impeded the involvement of developers and lenders in remediation of contaminated property.

In this article, rather than discuss brownfields or contaminated properties in general, we will describe in detail the evolution of a single brownfield property.

The History of Watersbend Apartments, 1984-1994

Watersbend is located on U.S. Highway 183 in northeast Austin along a creek. Improvements were constructed in 1984 at a cost of $13 million during a period of economic prosperity and unprecedented real estate construction in Austin. Watersbend was originally a 358-unit, garden-style complex of average-quality construction consisting of 25 buildings with wood frames on concrete slabs and a combination of brick and cedar siding. Amenities included two swimming pools, a clubhouse, and laundry rooms. The primary tenants were college students and middle-class families.

By the late 1980s, the Austin real estate market had collapsed. New tax rules, a slowing statewide economy overdependent on oil, and a glut of recently completed projects pushed the citywide apartment occupancy level below 80%. Watersbend suffered through this downturn along with other properties in Austin. At the turn of the decade, Watersbend and similar properties achieved a 90% occupancy level, albeit with rent levels well below those attainable in the period of 1984-1986.

Landfill Discovery and Tenant Evacuation

By 1991-1992, approximately 1,000 people called Watersbend home. Unbeknownst to residents, however, Watersbend was constructed over a closed municipal, solid-waste landfill. Reportedly, Travis County used the site and surrounding area as a county landfill from 1950-1960, and then the City of Austin used it as a landfill from 1960-1968. From 1966-1968, the city used much of the subject site for filling purposes, including most of the area where the apartment buildings would be constructed.

Two reports published prior to the construction of Watersbend described the landfill, but on the whole, recordkeeping on municipal landfills during this time was poor, and information regarding the landfill's boundaries, types and amounts of waste accepted, and environmental controls is sketchy and vague. Still, in the early 1980s, the project builder convinced the City of Austin that construction of the apartments over a closed landfill would not pose an undue health risk. The builder and architect asserted that the fireplace chimneys would properly ventilate residual methane gas emitted from the closed landfill. Absurd as that seems, the builder must have offered his explanation very persuasively because the apartments were completed within three years.

In 1991, environmental consultants performed the first known Phase I Environmental Site Assessment specific to Watersbend. The study revealed high concentrations of methane in two subsurface areas beneath the apartments. The report also raised concerns about structural settling, health problems caused by methane-gas migration into the apartment units, and leachate contamination of Walnut Creek.

The following year, officials with the Texas Natural Resource Conservation Commission (TNRCC) discovered unacceptably high levels of methane in several first-floor units. Because methane is odorless and colorless, the tenants could not have detected it themselves. While the risk of explosion was very low, the results of an explosion obviously would have been catastrophic. Within two days, state and local authorities forced the complete evacuation of the complex. This action received widespread publicity and exacerbated an already tight rental market.

In an instant, Watersbend became an insoluble liability to its owners. They defaulted on the loan, but the primary lienholder initially declined to foreclose on the property because it was unwilling to assume the risks of ownership. The property eventually became a foster child of the unwilling American taxpayer as a holding of the Resolution Trust Corporation (RTC).

The RTC's stewardship of Watersbend could best be described as indifferent. With security consisting of nothing more than a hastily constructed chain-link fence, the property was repeatedly vandalized and inhabited by squatters. Thieves stole most of the water heaters, appliances, carpet, and even doors and fireplaces. Vandals set some buildings on fire. Water damage from neglect and poor building design irreparably damaged many of the exterior walkways. As reported by the subsequent owner, the City of Austin used the property to train firefighters and in one case deliberately set one building ablaze, a SWAT team conducted exercises on the property. Both parties apparently believed they had clearance to destroy government property; whether they did is doubtful. In fact, the property had already been sold to a private developer when these incidents occurred. The developer received undisclosed compensation for the trespasses and damages.

Watersbend Purchased

In 1994, Limited Liability Corporation purchased Watersbend "as is" from the RTC for $1 million, or just $2,793 per unit. This sale price was drastically lower than prices of similar complexes built during the same period, as described in Table 1. If not for its evacuation and other problems, Watersbend probably could have sold for a price within the range of these comparable sales. In fact, Watersbend sold at a discount of 85%--90% compared to these properties.

These comparable transactions involved private parties, but at the time the RTC and other receivers were a dominant force in Austin real estate. Sales of similar properties from banks and the RTC ranged from $13,000-$15,000 per unit, indicating Watersbend sold for a discount of 79%-81% even when compared to properties with disadvantageous selling conditions.

To further illustrate the severity of the landfill's impact on the property, Table 2 describes five sales of apartment complexes that needed major rehabilitation and had a very low occupancy level.

These properties were chosen more for similarities in condition and vacancy than for similarities in age, size or location, but they effectively demonstrate the magnitude of the environmental problems beyond mere reconstruction. Watersbend sold at a discount of 13%-48% per unit compared to several cider, vacant or near-vacant apartments needing less extensive rehabilitation than Watersbend would ultimately require. Its sale price of $2,793 per apartment unit was roughly equivalent to the price of vacant land during 1994, indicative of a 100% loss in the contributory value of the improvements just ten years after their construction.

The Remediation of Watersbend Apartments, 1994-1999

The new owners faced an unusual obstacle in remediating Watersbend: the legal framework for doing so didn't exist. The State of Texas had few regulations specifically relating to the use of land over a closed landfill. "Brownfield" legislation and awareness were in their infancy, and existing laws covering environmentally challenged properties tended to be compulsory and punitive. Two measures were needed to spur the redevelopment of the property: the Voluntary Cleanup Program and Subchapter T, Chapter 330 of the Texas Administrative Code.

Voluntary Cleanup Program

The Voluntary Cleanup Program (VCP) is the primary program of Brownfield Redevelopment Initiative in Texas. According to the Texas Natural Resources Conservation Commission (TNRCC), the VCP "provides incentives for properties with real and perceived contamination [brownfields] to be investigated, cleaned, and redeveloped. An additional benefit is the sparing of outlying rural, 'greenfields.'" (5) The VCP was intended to be more proactive than punitive and provided a clearer, more streamlined approach to remediation than existing programs such as the State and Federal Superfund.

In brief, the owners of property in the VCP program must submit an application with an Environmental Site Assessment detailing the type and extent of contamination. Then the applicant and TNRCC must agree on the remediation process, and the applicant must pay all TNRCC oversight costs. After completion of the cleanup, the owner receives a Certificate of Completion from the TNRCC, stating that all non-responsible parties are released from all liability to the state for cleanup of areas covered by the certificate. Sites already under an enforcement order or pending legal action are not eligible for the VCP. More information about the VCP is available at <http://www.tnrcc.state.tx.us./permitting/trrp.htm>.

Subchapter T

In addition to the VCP, the Texas Legislature amended the state's Solid Waste Disposal Act, and the TNRCC enacted Subchapter T, Chapter 330 of the Texas Administrative Code in 1995. Both were written specifically with Watersbend in mind, and Watersbend became the pilot project for these statutes.

Subchapter T "establishes standards for the use and development of land over closed municipal solid waste landfills [and establishes] practical requirements while maintaining strict standards for human health and safety and environmental protection." (6) This statute does not cover hazardous wastes.

Subchapter T provides the TNRCC with authority to administer a permit program for construction of enclosed structures over a landfill, establish requirements related to their construction, establish procedures for conducting soil tests to determine the existence of a landfill, and provide notice to tenants of the landfill's existence.

In general, any permanent, enclosed structure within 1,000 feet of a waste disposal area must be designed and constructed to prevent gas migration- that is, the buildup of potentially explosive gases such as methane. The primary structural controls consist of layers of low gas permeability between the slab and the subgrade and a gas ventilation system to prevent buildup. Also required is a Site Operating Plan and a Structured Gas Monitoring Plan prepared by a professional engineer. The property owner must register the site in the county deed records, and the owner cannot lease property over a landfill without a permit from the TNRCC. Any waste excavated during redevelopment of the property must be disposed of in an approved landfill.

Owners are not obligated to investigate the existence of a landfill, but once known to them (whether by research or accident), they must immediately inform all tenants. The permit process is required regardless of the age of the landfill, although owners can suspend monitoring requirements if they can demonstrate no potential for gas migration. More information about Subchapter T is available at <http://www.tnrcc.state.tx.us/permitting/ wasteperm/mswperm/clseduse.html>.

The Remediation Process

In 1995, the owners of Watersbend presented a Comprehensive Assessment/Remediation Plan (CARP) to the TNRCC and submitted their application to the TNRCC's Voluntary Cleanup Program. The CARP and a Site Investigation Report were completed in 1996. The owners subsequently received approval to design a Remedial Action Work Plan (RAWP) consisting of three major components: a semiactive ventilation system consisting of 108 wells placed in ten clusters throughout the property, an active gas-extraction system in the subslab of each building that would prevent methane buildup in the apartment units, and a surface drainage-control system to prevent exposure to landfill leachate. Also, each apartment unit was provided a hard-wired, active gas monitor/alarm.

These three components cost just under $1.4 million, and the annual monitoring and maintenance cost was slightly under $40,000. In 1998, the TNRCC issued a conditional Certificate of Completion requiring the owners to monitor methane levels and operate a methane-gas recovery system for as long as minimum concentration levels are detected, estimated at the time to be fourteen years.

Concurrent with the Remedial Action Work Plan were slab leveling, repair of slab and beam cracks, provision of better drainage for foundations, rebuilding a retaining wall, and construction of a new retaining wall along Walnut Creek. These improvements were primarily related to the requirements of Subchapter T.

Three of Watersbend's 25 apartment buildings were deemed unfit for redevelopment and were demolished. Redevelopment of the remaining apartments took place in two phases during 1998 and 1999 and included new roofs, doors, windows, flooring, plumbing fixtures, and appliances. The demolition of the three buildings reduced the number of leasable units from 358 to 290.

Our firm was hired to appraise the property in early 1999 while remediation was underway and before any units were leased. We evaluated the risks and liabilities associated with the project and their effect on value, including:

The comprehensive redevelopment cost, including environmental remediation, was $9.5 million, or about $32,750 per unit. Until 1999, the owners paid for all remediation costs out-of-pocket. In 1999, the owners received a construction loan, but they had to provide personal guarantees and other real estate holdings as collateral.

Appraisal issues: Assessment of Market Acceptance, Ownership Risk, and Stigma

* Lack of market acceptance. Potential tenants, once notified of the property's history and ongoing monitoring as required by law, might refuse to live there;

* Legal compliance to the regulations of Chapter 330, Subchapter T of the Texas Administrative Code as described previously;

* Operation and maintenance of the active-gas extraction system and the semiactive-gas-extraction system as required by the conditional Certificate of Completion of the VCP;

* A $5 million insurance policy at a cost of $8,400 per year for five years. The policy covers legal expenses and pays off the primary lien in case of serious environmental problems during the life of the policy;

* The risk of future soil subsidence that could necessitate expensive repairs and maintenance;

* Watersbend's location amidst a larger brownfield area; and

* Other facets of stigma such as deed recordation of contamination (as required by Subchapter T and the risk reduction rules of the Voluntary Cleanup Program), the potential of third-party litigation instigated by adjacent property owners, and lender reluctance to fund additional loans due to the unique nature of the contamination and the remediation project.

Our task was to quantify those risks. Regarding the question of market acceptance, we researched similar situations including an apartment complex in southeast Austin. The property was also constructed over a landfill and had methane-buildup problems. While its remediation was not of the scale of Watersbend, the tangible signs that could affect its occupancy--a gas ventilation system, monitors, and in-unit alarms--were there. This property did not suffer any noticeable resistance from the market, and its occupancy and rent levels were equivalent to citywide rates. Our research of this property and other remediated dwellings indicated that a properly remediated property with active monitoring and other safeguards in place should not suffer more than minimal tenant resistance.

Still, the other risks and environmental liabilities were substantial. Even after completion of the remediation project, knowledgeable purchasers would demand a discount on this property in order to justify the investment risks and potential market resistance. These are defined by Randall Bell, MAI, in his book Real Estate Damages: An Analysis of Detrimental Conditions, as "the risk... associated with the ongoing stage of a detrimental condition analysis [including] the reluctance on the part of the real estate market to buy a property that has historically been damaged or tainted. Sometimes called stigma." (7)

The Case Studies Approach

Our firm quantified the discount with several case studies, that involved research of similar contaminated sales and remediated properties. The discount in each case study depended on the type and extent of contamination, the use of the property, the amount of governmental involvement, the extent of the remediation when sold, and whether the purchaser was indemnified by the seller or another party responsible for liabilities related to the contamination. In most cases, the discounts were quantified by comparison of the sale of the contaminated property with sales of unimpaired properties with similar physical characteristics and locations. Less frequently, comparison of the eventual sale price to an earlier contracted price with no disclosure or knowledge of contamination or lengthy marketing delays was the basis for the discount.

Each case study was rated for its similarity to Watersbend. Case studies with more severe contamination and less favorable circumstances were rated "higher," properties with relatively minor contamination and minor post-remediation stigma were rated "lower," and properties most similar to the subject were rated "even." The case studies are summarized in Table 3.

Case Studies 3, 4, and 5 were rated even and had a discount range of 10%-21%. These sites sold post-remediation or with only a minor threat of future contamination. Like Watersbend, two of the three sites were in the Voluntary Cleanup Program. Case Study 4 was the most similar to Watersbend; it involved an old landfill, was in the same stage of remediation before redevelopment, and required a similar amount of initial reinvestment capital. Case Study 8, although also involving a site analogous to a landfill, was rated higher because the materials were hazardous and the impact on properties surrounding the landfill was much greater when compared to Watersbend.

From these case studies, we estimated that the market value of Watersbend was 15% less than its unimpaired value. The quantified financial liabilities comprised approximately one-third (5%) of the discount, with the remaining two-thirds (10%) attributable to the other risks described in the bulleted list at the beginning of this section.

Watersbend Reopens

After rehabilitation and remediation were partially completed at Watersbend, the complex was renamed "Salado at Walnut Creek" to avoid the negative association with the "Watersbend" moniker. In September 1999, leasing began on 110 rehabilitated units, while rehabilitation continued on the remaining 180 units. Pursuant to Subchapter T, leasing agents informed potential tenants in writing that the property was once used as a municipal solid waste landfill and that structural controls were in place to minimize the dangers posed by the former landfill.

According to the leasing manager at Salado at Walnut Creek, the complex received little resistance from potential tenants due to the written disclosure, despite local media coverage of the reopening that was skeptical, if not acutely unfavorable. In truth, some of the lack of resistance could be attributed to the condition of Austin's apartment market, which was experiencing historically high levels of rent and occupancy. Arguably, a weaker market might have produced more resistance because potential tenants would have more available housing options. The inference is that brownfield redevelopment projects need a strong economic climate to overcome the multiple risks involved.

Approximately 100 of the 110 available units were leased between September and October 1999 while remediation approached completion on the remaining units. By February 2000, 70% of the full 290 units were occupied or pre-leased. By July 2000, when redevelopment was completed and all 290 units were available for leasing, the complex attained a 94% occupancy rate. As of 2001, the project's occupancy was near 95%, equivalent to citywide averages, and the units leased for rates at the upper end of the range of competitive properties.

Conclusion

After the remediation was complete and the property was fully leased, additional appraisals have confirmed that the residual stigma has diminished to [+ or -] 10%. This ownership risk, small but still present, makes the property slightly less attractive to potential investors despite the healthy rent and occupancy levels because of ongoing legal requirements of Subchapter T and the VCP, annual expenditures for environmental monitoring costs for at least another twelve years, and deed recordation and disclosure requirements. Also, the property may be hurt more than comparable apartments in the event of a market downturn because much of the property's success is tied to the strong economic climate in which it reopened. Nevertheless, we concluded that the property value exceeds its redevelopment costs, and extensive redevelopment may make it more valuable today than projects of comparable age and construction.

As of late 2001, the stigma of ownership risks is slight and declining. In the spring of 2001, the property owners secured a new, permanent loan requiring an environmental insurance policy covering additional pollution conditions. These conditions could cause loss of use and legal expenses for defense of any third party lawsuits stemming from residual contamination at the property; however, this policy does not cover loss in market value. The cost of this insurance policy (amortized over ten years), combined with the ongoing environmental monitoring costs, reduces the net annual operating income by three to four percent and is a large, tangible component of the residual property stigma. Over time, the stigma should continue to decrease, although it may never reach zero. This unusual brownfield redevelopment project should serve as a model to numerous parties: to developers needing a framework to remediate and market contaminated properties, to municipal planners pursuing creative solutions to increase the local tax base, and to appraisers seeking insights into post-remediation property values and stigma.
Table 1

Comparison of Watersbend Sale to Sales of Unimpaired Apartment Complexes

Apartment Date of Year SF/ Monthly
Complex Sale Built Units Unit Rent/SF Occupation %

Watersbend Jan-94 1984 358 707 NA 0%
Shadow Wood Jul-93 1984 240 735 0.68 99%
Villas of
La Costa Feb-93 1979 204 780 0.68 100%
Stony Creek
Landing Apr-94 1982 420 750 0.66 95%
Chevy Chase
Downs Apr-94 1985 240 678 0.72 95%
Wildcreek Apr-94 1984 232 663 0.68 92%

Apartment Sale Price/
Complex Price Unit

Watersbend $1,000,000 $2,793
Shadow Wood 6,000,000 25,000
Villas of
La Costa 4,250,000 20,833
Stony Creek
Landing 11,200,000 26,667
Chevy Chase
Downs 5,275,000 21,979
Wildcreek 4,425,000 19,073
Table 2

Comparison of Waterbend Sale to Sales of Apartment Complexes in Need of
Major Rehabilitation

Apartment Date of Year Occupation Sale
Complex Sale Built Units SF/Unit % Price

Watersbend Jan-94 1984 358 707 0% $1,000,000
2506 Manor Road Jan-93 1971 102 360 0% 455,000


Greentree Aug-93 1973 124 869 0% 400,000

South Shore May-91 1963, 145 732 0% 778,000
 1973


Riverpark Jan-91 1968- 490 873 23% 1,690,000
 1972

Estrada Nov-92 1968 310 839 30% 1,600,000



Apartment Price/
Complex Unit Notes

Watersbend $2,793 Subject property
2506 Manor Road 4,461 Former affordable housing
 project; abandoned,
 100% vacant
Greentree 3,226 Vacant for five years; $6,000/
 unit rehabilitation
South Shore 5,366 $10,000-$12,000/unit
 rehabilitation including
 asbestos and gas line leaks
 which closed the property
Riverpark 3,449 $7,100/unit in rehabilitation/
 repairs: appliances, flooring,
 paint, exterior fences, roofs
Estrada 5,161 Bank sale; water damage
 from roof/window leaks,
 only 33% inhabitable
Table 3

Contaminated Case Studies



# Location Property Type Waste Type

1 Austin, TX Thousands of Gasoline and other
 residences and petroleum products
 businesses surrounding
 a petroleum storage
 facility
2 Austin, TX Motel and conference Asbestos, petroleum
 center hydrocarbons


3 Austin, TX 9.3-acre vacant Hydrocarbons from
 commercial lot near crude oil spill
 former gas station off-site


4 Dallas, TX 18.6-acre vacant Municipal solid waste
 commercial tract from old landfill


5 Houston, TX 1.5-acre vacant Benzene, lead,
 downtown lot phthlate


6 Houston, TX Apartment complex Gasoline, petroleum
 next to gasoline hydrocarbons
 service station



7 Keller, TX 22-acre, multiuse Petroleum
 property on former hydrocarbons and
 gas station site heavy metals in soils

8 Houston, TX Housing subdivision Creosote, heavy
 near Superfund metals, sludges,
 Site (chemical waste petroleum
 storage facility) hydrocarbons




 Severity of Contamination
 Amount of and Post-Remediatlon Situa
# Location Discount tion Compared to Watersbend

1 Austin, TX 25.0% HIGHER: Legal action against oil
 companies; contamination of air,
 soil and groundwater; 14-year
 remediation timetable

2 Austin, TX 28.0% HIGHER: Contaminated by on-site
 asbestos and hydrocarbons from
 offsite source; no hydrocarbon
 remediation has occurred
3 Austin, TX 13.5%; EVEN: Contamination on adjacent
 16.0%-21.0% site; discount caused by testing
 costs, marketing delays, and
 marketing delays, and future
 monitoring costs
4 Dallas, TX 10%-20% EVEN: Circumstances very similar
 to subject property; future
 buildings require gas-extraction
 systems
5 Houston, TX 20.0% EVEN: Property in Voluntary Cleanup
 Program; discount consisted of
 escrow against potential future
 liabilities
6 Houston, TX 33.3% HIGHER: Sale price negotiated
 before full extent of
 contamination service station
 was known; risk of off-site
 migration and other contamination
 issues
7 Keller, TX 25.8% HIGHER: Probable greater extent of
 contamination with no pre-sale
 remediation; fallout of prior
 contract
8 Houston, TX 33.0%-50.0% HIGHER: Properties near a
 Superfund Site with extensive
 public disclosure; remediation
 alternatives included
 incineration, natural attenuation,
 excavation and removal of soils


Internet Links

TNRCC Brownfield Redevelopment Initiative Home Page: <http://www.tnrcc.state.tx.us./permitting/remed/vcp/brownfields.html. >.

TNRCC Voluntary Cleanup Program (includes links to Texas VCP News, guidance publications, Applications and Agreement forms, and examples of Certificates of Completion): <http:/www.tnrcc.state.tx.us./permitting/remed/vcp index.html>.

TNRCC Risk Reduction Program (for the VCP): <http://www.tnrcc.state.tx.us./permitting/ trrp.htm>.

EPA Region 6 Brownfield Program: <http://www.epa.gov/ earth1r6/6sf/bfpages/sfbfhome.htm>.

City of Austin Brownfield Redevelopment Program: <http://www.ci.austin.tx.us/watershed/brownfields.htm>.

City of Dallas Brownfield Redevelopment Program: <http://www.dallascityhall.com/dallas/html/brownfields_.html>.

City of Fort Worth Economic Redevelopment Program: <http://ci.fort-worth.tx.us/dem/brownfields.htm>.

City of Houston Brownfield Redevelopment Program: <http://www.gcr1.com/epa/pilotcities/default.cfm?ObjID=114>.

City of San Antonio Brownfield Assessment Pilot: <http://www.epa.gov/swerosps/bf/html-doc/sananton.htm>.

Brownfield News: <http://www.brownfieldnews.com/>.

(1.) Peter Patchin, "Contaminated Properties Stigma Revisted," The Appraisal Journal (April 1991): 162-172.

(2.) Bill Mundy, MAI, PhD, "The Impact of Hazardous Materials on Property Value," The Appraisal Journal (April 1992): 155-162.

(3.) Michael V. Sanders, "Post-Repair Diminution in Value from Geotechnical Problems, The Appraisal Journal (January 1966): 59-66.

(4.) Robert Simons, PhD, Turning Brown fields into Greenbacks, Urban Land Institute (1998).

(5.) <http://www.tnrcc.state.tx.us./permitting/remed/vcp/brownfields.html> .

(6.) <http://www.tnrcc.state.tx.us/permitting/wasteperm/mswperm/clsdinfo.p df>

(7.) Randall Bell, Real Estate Damages: An Analysis of Detrimental conditions (Chicago: Appraisal Institute, 1999).

References

Avens, Scott B. "The Valuation of Defective Properties: A Common Sense Approach." The Appraisal Journal (1997).

Bell, Randall MAI. "Real Estate Damages: An Analysis of Detrimental Conditions." The Appraisal Institute (1999).

Mundy, Bill. "Stigma and Value." The Appraisal Journal (January 1992): 7-13.

Mundy, Bill. "The Impact of Hazardous Materials on Property Value." The Appraisal Journal (April 1992): 155-162.

Mundy, Bill. "The Impact of Hazardous and Toxic Material on Property Value: Revisited." The Appraisal Journal (October 1992): 463-471.

Patchin, Peter. "Contaminated Properties Stigma Revisited." The Appraisal Journal (April 1991): 162-172.

Patchin, Peter. "The Valuation of Contaminated Properties." Real Estate Issues (Fall/Winter 1991): 50-54.

Rinaldi, A. "Contaminated Properties--Valuation Solutions." The Appraisal Journal (July 1991): 377-381.

Sanders, M. "Post-Repair Diminution in Value from Geotechnical Problems." The Appraisal Journal (January 1996): 59-66.

Simons, Robert. Turning Brownfields Into Greenbacks. (Washington, D.C.: Urban Land Institute, 1998).

Simons, Robert, and Heidi G. Robertson. "Deed Restrictions and Other Institutional Controls as Tools to Encourage Brownfield Redevelopment." Environmental Law and Practice (Summer 1999).

Simons, Robert, and Paul Syms. "Contaminated Land: Do Property Registers Do More Harm Than Good? An Analysis of the UK and USA Approaches to Public Management of Brownfields." (Land Contamination and Reclamation UK, 1999).

Simons, Robert. "How Many Brownfield Sites are There?" Journal of Public Works Management and Policy (2:3, 1998).

Simons, Robert, and Michael Leccese. "Brass Mill Mall: Bringing New life to a Brownfield Site in Waterbury; Connecticut." Urban Land (June 1998).

Simons, Robert, and Don Iannone. "Supply and Demand for Brownfields in Great Lakes Cities." Urban Land (June 1997).

Simons, Robert. "Financing Environmentally Contaminated Land in the Great Lakes Empowerment Zones." Economic Development Commentary (Fall 1996).

Rudy R. Robinson, Ill, MAI, is the president of Austin Valuation Consultants, Inc., in Austin, Texas. Mr. Robinson specializes in appraising environmentally contaminated properties, especially for litigation purposes. He has been published twice in The Appraisal Journal and is a frequent guest speaker at real estate conferences and seminars. He graduated from the University of Texas at Austin with a bachelor of arts.

Contact: RRR@austinval.com.

Scott R. Lucas is a former senior associate for Austin Valuation Consultants. He is a graduate of the University of Texas at Austin with a bachelor's degree in real estate and urban land development.

Contact: SRL@texas.net.

Garland G. Resberry is a senior associate for Austin Valuation Consultants. He graduated from the University of Texas at Austin with a bachelor's degree in finance.

Contact: rasberry@austinval.com.
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Title Annotation:real estate
Author:Robinson, Rudy R.; Lucas, Scott R.; Rasberry, Garland G.
Publication:Appraisal Journal
Article Type:Statistical Data Included
Geographic Code:1USA
Date:Jul 1, 2002
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