Clackamas County Assessor v. Geary

Oregon Tax Court·Decided September 21, 2012·No. TC-MD 120298D·Unpublished

Opinion

IN THE OREGON TAX COURT

MAGISTRATE DIVISION

Property Tax

CLACKAMAS COUNTY ASSESSOR, )

)

Plaintiff, ) TC-MD 120298D )

v. )

)

KEVIN GEARY, )

)

Defendant. ) DECISION

Plaintiff appeals the 2011-12 real market value of property identified as Account 05003823 (subject property). A telephone trial (uncontested) was held on July 26, 2012. Todd Cooper (Cooper), Registered Appraiser, appeared and testified on behalf of Plaintiff.

Plaintiff’s Exhibits 1 through 7 were admitted without objection.

I. STATEMENT OF FACTS

The subject property is a farmhouse style single family home that sits on 1.47 acres of land in Northeast Clackamas County. (Ptf’s Ex 1 at 4.) The home is 3,832 square feet with two stories, six bedrooms, and two bathrooms. (Id.) The home “was originally constructed around the turn of the century and has had several subsequent additions and remodels. The most recent addition was a 960 square foot area added in 2005.” (Id.) Cooper testified that the subject property has good access to highway and freeway systems, shopping centers, employment centers, and recreational centers.

Cooper testified that on December 6, 2000, approximately 300 gallons of heating oil were mistakenly pumped into the subject property’s basement through an abandoned fill pipe that had once been connected to a heating oil storage tank. (Ptf’s Ex 6 at 3.) Cooper testified that the Department of Environmental Quality (DEQ) report stated that the oil spill contaminated the soil

DECISION TC-MD 120298D 1 below and around the subject property’s basement floor. (Id.) Cooper testified that DEQ approved contractor Foss Environmental performed a “phase I investigation” and “phase II mitigation and clean-up” of the subject property. (Ptf’s Ex 1at 17.) Foss Environmental completed Phase I on March 16, 2001, and Phase II on May 16, 2001. (Ptf’s Ex 6 at 3.) Cooper testified that Foss Environmental’s “Remedial Investigation Report” dated July 2001, identified “no impacts to nearby domestic well” and “no residual risk from heating oil constituents using a risk-based analysis.” (Id.) After inspecting the subject property on June 11, 2002, “DEQ determined that no further remedial action was required.” (Id.)

Plaintiff appeals the Board of Property Tax Appeals (BOPTA) Order, dated March 13, 2012, determining a real market value of $100,000. (Ptf’s Compl at 2.) According to the BOPTA Order, the subject property’s maximum assessed value is $313,163. (Id.) Cooper testified that Plaintiff is requesting a real market value of $367,189 as of January 1, 2011.

Cooper testified that during the BOPTA hearing on February 6, 2012, the owner of the subject property testified that the subject property was stigmatized from the contamination that occurred in December 2000. Cooper testified that the owner of the subject property did not provide BOPTA with any evidence indicating that the property suffered from a long term stigma. Cooper testified that as a result of the BOPTA hearing, BOPTA reduced the real market value of the subject property from $367,189 to $100,000. (Ptf’s Compl at 2.)

Cooper testified that he performed market research “to determine if a negative adjustment was appropriate due to [the] prior contamination.” (Ptf’s Ex 1 at 17.) Cooper testified that he began his research with 30 previously contaminated properties, and then narrowed the sample to the six properties most comparable to the subject property based on type and degree of contamination. Cooper testified that he compared the six properties’ sale prices with their real

DECISION TC-MD 120298D 2 market values assigned by the county. Cooper testified that he found that all of the previously contaminated properties sold for prices higher than the county’s real market tax roll values. (See Ptf’s Ex 7 at 1.) Cooper testified that his “research indicated that once the contamination is properly remediated (and certified by D.E.Q.) and given adequate seasoning time of 12-36 months with no further reported contamination, similarly contaminated properties have sold at or very near market values and with marketing times typical of non-contaminated properties.” (Ptf’s Ex 1 at 17.) Cooper testified that his research found no long term stigma attached to previously contaminated properties that are comparable to the subject property.

Cooper testified that he considered the three valuation approaches in determining the subject property’s 2011-12 real market value. (Ptf’s Ex 1 at 11.) Cooper testified that “[t]he income approach was considered, but [was] not felt to be a credible indicator of market value as homes in the subject area are generally acquired for owner occupied, single family use rather than as income producing properties.” (Id.)

Cooper testified that “[t]he cost approach indicates a value for the subject property of $367,189 as of 01/01/2011.” (Ptf’s Ex 1 at 11.) Cooper testified that “[t]he cost approach is the basis for the original valuation of the subject property for tax assessment purposes for January 1, 2011 * * *.” (Id. at 17.) Cooper testified that the county’s original valuation of the subject property supports a real market value of $367,189. (Ptf’s Compl at 2.) Cooper testified that he included the $367,189 as the cost approach value in his appraisal report, but did not perform a new cost approach valuation. Cooper testified that the cost “valuation approach is typically more reliable with newly constructed homes * * * therefore the cost approach was given less weight in the final reconciliation.” (Ptf’s Ex 1 at 11.) ///

DECISION TC-MD 120298D 3

Cooper testified that the sales comparison approach “supports a final estimate of value for the subject property of $415,000 as of 01/01/2011.” (Ptf’s Ex 1 at 11.) Plaintiff submitted the sale prices for five comparable properties as evidence of the subject property’s real market value.1 (Ptf’s Ex 1 at 5.) The sale prices range from $317,500 to $465,000. (Id.) Cooper testified that he adjusted each comparable property’s sale price to accurately reflect the conditions of the subject property. The sale prices of Comparable # 2, # 3, # 4, and # 5 were increased $81,300 (22.2 percent), $27,800 (7.5 percent), $32,540 (8.6 percent), and $76,040 (23.9 percent) respectively. (Id.) The sale price of Comparable # 1 was decreased $24,500 (5.3%). (Id.) The adjusted sale prices range from $393,540 to $447,800. (Id.)

The subject property is “located in an area that experienced a decline in property values for the twelve months prior to the effective date of appraisal.” (Ptf’s Ex 1 at 15-16.) Cooper made adjustments “based upon the estimated rate of decline of 8.0% over the prior twelve months.” (Id. at 16.) Adjustments for differences in above grade finished living area and differences in garage area were made at the rates of $40.00 per square foot and $10.00 per square foot respectively. (Id.) Cooper increased the sale price of Comparable # 1 by $2,500, because the property lacked central air conditioning. (Id.) Cooper decreased the sale prices of Comparables # 1 and # 4 by $35,000 each, because the properties were remodeled and in better condition than the subject property. (Id.) Cooper decreased the sale price of Comparable # 3 by $15,000, because the property “included a small finished guest quarters area at the time of sale.” (Ptf’s Ex 1 at 17.) Cooper did not make adjustments for lot size and age differences. (Id. at 16.) Cooper explained that “the subject and comparable [lots were] felt to be functionally equal,” and “[t]he subject and comparable sales [were] felt to be of similar overall effective age * * *.” (Id.)

1 Plaintiff did not include any of the six previously contaminated properties as one of the five comparable properties analyzed to determine the subject property’s real market value.

DECISION TC-MD 120298D 4

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