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Forensic Applications Consulting Technologies, Inc. POST- DECONTAMINATION REPORT of an Identified Illegal Drug Laboratory at: 1809 Lydia Drive Lafayette, CO 80026 Prepared for: Christina M. Eisert 1027 Mahlon Ct. Lafayette, CO 80026-1828 Prepared by: Forensic Applications Consulting Technologies, Inc. 185 Bounty Hunter’s Lane Bailey, CO 80421 January 27, 2015
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Page 1: POST- DECONTAMINATION REPORT of an Identified Illegal Drug ...forensic-applications.com/meth/Lydia_Post_Decon_Report.pdf · Forensic Applications Consulting Technologies,Inc. POST-

Forensic Applications Consulting Technologies, Inc.

POST- DECONTAMINATION REPORT of an

Identified Illegal Drug Laboratory at:

1809 Lydia Drive Lafayette, CO 80026

Prepared for:

Christina M. Eisert 1027 Mahlon Ct.

Lafayette, CO 80026-1828

Prepared by:

Forensic Applications Consulting Technologies, Inc. 185 Bounty Hunter’s Lane

Bailey, CO 80421

January 27, 2015

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Table of Contents EXECUTIVE SUMMARY ................................................................................................................. 3

Subject Structure ......................................................................................................................... 3 REGULATORY REQUIREMENTS .................................................................................................. 5

County Requirements.................................................................................................................. 5 State Requirements..................................................................................................................... 5

Governing Body ...................................................................................................................... 6 SAMPLE COLLECTION .................................................................................................................. 6

Wipe Samples ............................................................................................................................. 6 Methamphetamine Analysis ........................................................................................................ 7 QA/QC Precautions ..................................................................................................................... 7

Field Blanks .................................................................................................................... 7 Field Spikes .................................................................................................................... 8

Cross Contamination .......................................................................................................... 8 Sample Locations ................................................................................................................... 8

Sample Results ................................................................................................................ 13 CONCLUSIONS ............................................................................................................................ 15 Appendix A: Supporting Documents Appendix B: Analytical Reports for FACTs Samples Appendix C: Contractor’s Submittals Appendix D: Compact Digital Disk

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EXECUTIVE SUMMARY On December 15, 2014, at the request of a potential buyer, a property assessment for the presence of methamphetamine was conducted at 1809 Lydia Drive, Lafayette, CO 80026 (the subject property) by Weecycle Environmental Consulting, Inc. (WEC). The WEC employee was not authorized to do such assessments and virtually no aspect of State regulations was followed, and therefore, the assessment performed by WEC at this property was unlawful. During the unlawful assessment, the unauthorized consultant identified trace levels of methamphetamine at the property. Forensic Applications Consulting Technologies, Inc. (FACTs) was subsequently contracted to perform a legitimate “full clearance assessment” as specified in Section 6 of the State regulations. That assessment indicated the presence of methamphetamine contamination in excess of the regulatory limits in eight areas of the subject property. Between the dates of December 31, 2014 and January 14, 2015, Crystal Clean Decontamination performed decontamination services at the property. On January 14, 2014, FACTs performed a post-decontamination assessment as mandated in State Regulation 6 CCR 1014-3. Based on the totality of circumstances, FACTs concludes: • An illegal drug laboratory, as defined in Colorado Revised Statutes,§25-18.5-101(8) existed at the property since at least December 15, 2014, until the receipt of the post decontamination samples. • Based on the clearance sampling at the subject property in accordance with 6 CCR 1014-3, Part 1, § 6, the cleanup standards established by 6 CCR 1014-3, Part 1, § 7 have been met.

• Clearance sampling was performed and this report was prepared by Mr. Caoimhín P. Connell, Forensic Industrial Hygienist with FACTs. Mr. Connell was assisted in the field by Ms. Christine Carty, 1 President of FACTs. • This final “Post-Decontamination Report” includes a variety of other documents found on the digital disc that accompanies this report. The disc is an integral part of the report and contains, by reference, many of the required elements for a final report.

Subject Structure For the purposes of 6 CCR 1014-3, the property is a 2,132 square foot property not including a 630 square foot attic, and a second 484 square foot attic above the garage. During the performance of the December 22, 2014 Preliminary Assessment, public records from the Assessor’s Office were ambiguous which lead to ambiguities in GPS,

1 Training certificate in Clandestine Drug Laboratory Assessments through the Colorado Regional Community Policing Institute, Colorado Division of Criminal Justice, (US Dept. of Justice High Intensity Drug Trafficking Area). Certified pursuant to 29 CFR §1910.120.

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GIS and other directional services. As such, based on the best information available, FACTs presented aerial photographs of the structure. Based on more accurate information, we believe the structures thus depicted were incorrect. Therefore, we are correcting the Preliminary Assessment aerial photograph with the following aerial photograph which we believe properly depicts the correct structure.

Figure 1

General Site Layout2 Although only eight areas in the property required decontamination, the contractor elected to isolate only three compliant areas and clean all remaining areas. The three compliant areas that were isolated were: 1) Force air furnace system 2) Attic above garage 3) Attic above residence All other areas not listed above were cleaned.

2Possible Copyright by Google; fair use exemption accessed through Google Earth™

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REGULATORY REQUIREMENTS

County Requirements Boulder County, CO adopted Ordinance 2006-1 concerning methamphetamine contamination in vehicles and structures. Certain aspects of the Boulder County ordinance are contrary to State requirements and the county ordinance creates some conflicts with state regulations. In any event, Boulder County does not enforce State or County Regulations, and actively condones violations of statutes and regulations, both criminal and civil and will not be considered further.

State Requirements Following property decontamination, State regulation 6 CCR 1014-3 Amended requires specific activities that must be completed, specifically: General Sampling Requirements Rubric Action Status 6.9.1 Has at least 400 cm2 of surface area been sampled from every room 6.9.1 Has at least 400 cm2 of surface area from each attic 6.9.1 Has at least 400 cm2 of surface area from each crawlspace NA 6.9.2 Has at least 800 cm2 of total surface been sampled from the property 6.9.3 Has an additional 100 cm2 of surface area been sampled for each additional

500 ft2 greater than (or fraction thereof) 500 ft2?

6.9.4

Has 100 cm2 of the heat exchanger unit been sampled? Has 100 cm2 of the cold air return system been sampled? Has 100 cm2 of the supply air system been sampled? Has 100 cm2 of a fourth elective been sampled? Photo documentation to verify that the ventilation system has been cleaned and is free of debris? NA

6.9.5 Has one discrete sample been collected from each non-ducted heating, cooling or circulating unit? NA

6.9.7 Has the interior of all major appliances (microwaves, refrigerators, freezers, ovens, and dryers) been sampled?

Single Family Dwellings:

Rubric Action Status 6.9 Have all structures on the property been sampled?

Multi-unit building

Rubric Action Status

6.9 If there is exclusive access to any auxiliary portion of the multi-unit property (such as a storage room or garage): Have all such auxiliary structures been sampled?

NA

Buildings and structures whose internal walls were removed during decontamination, or for structures with no rooms.

Rubric Inclusion Status

6.9.10 6.9.10 For structures that have no rooms, the Consultant shall sample at least 100 cm2 of surface area for every 500 ft2 of floor space. . NA

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Elements of Final Postdecontamination Report Rubric Inclusion Status

4.11.1 Have the limitations on access of a contaminated shared attic in a multi-unit structure been documented? NA

4.11.1 Does the final report contain language about contacting the HOA regarding contaminated shared attic in a multi-unit structure? NA

4.11.2 Have the limitations on access of a contaminated shared crawlspace in a multi-unit structure been documented? NA

4.11.2 Does the final report contain language about contacting the HOA regarding contaminated shared crawlspace in a multi-unit structure? NA

4.12 Have the limitations on access of a contaminated shared ventilation system in a multi-unit structure been documented? NA

4.12 Does the final report contain language about contacting the HOA regarding contaminated shared ventilation system in a multi-unit structure? NA

8.1 Does the final report contain the Preliminary Assessment Report (or a summary of the information and findings presented therein).

8.2 Photographic documentation of post-decontamination property conditions. 8.3 A description of the sampling procedures used, including sample collection,

handling, and QA/QC.

8.4 Documentation of the analytical methods used, laboratory QA/QC documentation, laboratory report and chain-of-custody.

8.5 Results of post-decontamination clearance sampling 8.5 Computer generated figure of post-decontamination clearance sampling 8.6 Date FACTs received Contractor’s “Decontamination Summary Report” 01/26/15 8.7 Evidence of Consultant certification. 8.8 Signed mandatory language of certification 8.9 Date copy provided to the property owner 1/27/15 8.9 Date copy provided to the Contractor 1/27/15 8.9 Date copy provided to the Department (on or before) 2/26/15 8.10 Date copy provided to the Governing Body 1/27/15

Governing Body For this property, jurisdiction for the abatement of the public nuisance lies with the office of the “Governing Body.” The property lies within Boulder County, and pursuant to CRS §25-18.5-101(7), the office of the “Governing Body” is: Michael Richen, CIH Boulder County Public Health Administration/Environmental Health Site 3450 Broadway Boulder, CO 80304

SAMPLE COLLECTION

Wipe Samples The collection of the samples was performed as described in Section 6 of 6 CCR 1014-3. Exclusively discrete samples were collected for this property with the exception of the forced air system which must, by regulation, (§6.7.1.1.) be a composite sample.

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The sample locations were identified by the Industrial Hygienist based on regulatory requirements, which disallow valid standard Industrial Hygiene decision making processes. As such, since the sampling is designed to satisfy regulatory requirements, FACTs cannot guarantee the validity or appropriateness of the samples or their results, and the samples are interpreted exclusively within the context of the regulations. The wipe sample medium was commercially available cotton-poly mixed wipes impregnated with USP isopropyl alcohol. Each proposed sample area was delineated with a measured outline, in compliance with §6.2.2. The wipe samples were collected by methodically wiping the entire surface of the selected area with moderate pressure; first in one direction and then in the opposite direction, folding the gauze to reveal fresh material as necessary. The samples were returned to their independent centrifuge tube and capped with a screw-cap.

Methamphetamine Analysis The wipe samples were submitted under the special regulatory chain-of-custody for analysis to Reservoirs Environmental Laboratories in Denver, CO for analysis by GCMS.3 The special regulatory chain-of-custody is not a normal chain of custody but rather contained the additional regulatory requirements found in Sections §6.2.14.1 through §6.2.14.12

QA/QC Precautions The regulations prohibit the application of standard scientifically valid Industrial Hygiene QA/QC methodologies, and therefore, FACTs employed the mandatory regulatory QA/QC provisions instead.

Field Blanks Field blanks were collected and submitted for analysis pursuant to the requirements of the regulations (which are contrary to good sampling practices). The utility of fields blanks, collected pursuant to State regulations is no longer valid, unless the results are below detection limits. Under normal, standard sampling environmental protocols, there are various types of “blanks.” The purpose of the field blank is to determine if the sampling materials and the handling procedures contributed to the presence of any contaminant identified. According to the new State regulations (Section 6.2.12.1), however, the Industrial Hygienist is required by regulations to open and expose the field blank in a contaminated property, and literally wave the sampling materials around in the potentially contaminated air. Therefore, if contaminant is identified in the field blanks, one would never know if the reported contamination was due to tainted sampling materials and poor handling, or if the reported contamination was the result of

3 The laboratory essentially uses the NIOSH Method 9106 “METHAMPHETAMINE and Illicit Drugs, Precursors and Adulterants on Wipes by Liquid-Liquid Extraction”

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contamination after the blank had been exposed to/coming into contact with contamination while opening the field blank in a contaminated property and waving the sampling materials around in the potentially contaminated air. Similarly, pursuant to State regulations, the Industrial Hygienist is required to make every 11th sample and the last sample a field blank. In this way the ability to submit surreptitious blanks to check the laboratory efficacy is lost.

Field Spikes Field spikes are used to evaluate the laboratories ability to properly recover analyte from the samples, and to evaluated the parameter of “bias,” as well as accuracy and precision. However, the regulations state:

§3.7.6.3 … Spiked samples submitted for analysis shall not be used for purposes of compliance with the regulation.

Since the regulatory sampling protocol is not scientifically based, but is based on meeting arbitrary regulatory parameters, no statement regarding bias, precision or accuracy can be made outside of the claims of the laboratory itself. Therefore, no further interpretation is attempted. All other QA/QC considerations are provided in the accompanying laboratory report without interpretation.

Cross Contamination Prior to entering the property, the Industrial Hygienist and his Technician donned disposable Tyvek booties. Prior to the collection of each specific sample, a fresh pair of surgical gloves was donned to protect against the possibility of cross contamination. The pliable ruler used to measure each surface area was decontaminated with a single-use disposable alcohol wipe between samples; alternatively for some samples, single use disposal painter’s tape was applied to delineate the sampling area.

Sample Locations In the following drawings, FACTs has presented the locations of the Clearance Assessment samples. In the Preliminary Assessment, the compass directions were determined using the information on GIS sources. As a result, the compass directions in the drawings of the PA were erroneously rotated 90° clockwise. The compass directions in the following drawings are corrected. In the following figures, shaded sample indicators (triangles) indicate the samples collected during the initial sampling phase on December 22, 2014.

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Figure 2

Main Attic Sample Location

Figure 3

Garage Attic Sample Locations

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Figure 4

Second Floor Sample Locations

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Figure 5

Ground Floor Sample Locations

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Figure 6

Basement Sample Locations

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Sample Results The state regulations appear to have been written without editorial assistance so that even the word “methamphetamine “ was misspelled on official documents;4 one of the requirements of these regulations (§3.7.6.3) is that “…sample results shall be presented as reported by the analytical laboratory, and shall not be adjusted, changed, or manipulated in any way.” Therefore, for the purposes of meeting this requirement, the following figure is presented:

Figure 7

December 22, 2014 Sample Results Pursuant to §3.7.6.3

4 See for example, http://www.forensic-applications.com/meth/CDPHE_Meth_Blank.pdf

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Figure 8

January 14, 2015 Sample Results Pursuant to §3.7.6.3 Obviously, however, in order to know which sample came from where, and compare the sample results with regulatory levels, at some point the sample results must be converted to units that are germane to the regulations. Therefore, in the following table, we have presented the data in units germane to the interpretation of the same for comparison against State levels. State regulations no longer permit an Industrial Hygiene interpretation of the data, and none is presented. The shaded samples were those clearance samples collected on December 22, 2014. All results are in µg/100cm2 unless otherwise indicated.

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Sample Number Location Area

Sampled Results

µg/100cm2 LM122214-10 Field Blank NA <0.05* LM122214-13 Furnace composite 400 0.29 LM122214-20 Field Blank NA <0.05* LM122214-22 Main Attic PVC pipe 400 0.25 LM122214-23 Garage attic cleats 400 0.17 LM122214-25 Field Blank NA <0.05* LM011415-01 Ground floor main area N wall 500** 0.01 LM011415-02 Interior of kitchen refrigerator 400 <0.01 LM011415-03 Interior of kitchen stove 400 <0.01 LM011415-04 Interior of dishwasher 400 <0.01 LM011415-05 Ground floor powder bath, door frame 400 <0.01 LM011415-06 Basement Rec room, N wall, east end 400 0.02 LM011415-07 Basement under stairs back of door 400 <0.01 LM011415-08 Basement pantry inside door 400 <0.01 LM011415-09 Basement bathroom, floor 400 0.01 LM011415-10 Basement utility room back of door 400 <0.01 LM011415-11 Field Blank NA <0.05* LM011415-12 Upstairs hall, E wall, E end above BR door 400 <0.01 LM011415-13 Upstairs common bath, East wall 400 <0.01 LM011415-14 Upstairs northwest bedroom, back or door 400 0.06 LM011415-15 Upstairs northeast bedroom, back or door 400 0.02 LM011415-16 Upstairs south bedroom, back or door 400 <0.01 LM011415-17 Master bathroom door frame 400 0.03 LM011415-18 Garage plumbing cover 400 <0.01 LM011415-19 Field Blank NA <0.05*

* Absolute micrograms recovered. The “<” symbol indicated “less than.” ** Room size was greater than 500 ft, but less than 1,000 ft2.

Table 1 Sample Results in Concentration

CONCLUSIONS Based on the totality of circumstances, the property is compliant with the regulatory requirements of 6 CCR 1014-3, and this report is the Consultants certification of compliance as specified in State regulations 6 CCR 1014-3 and by CRS 25-18.5-103 (2)(a). (Please see additional compliance information on the accompanying disc).

-*END*-

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Appendix A Supporting Documents

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Forensic Applications Consulting Technologies, Inc. Certification, Variations and Signature sheet FACTs project name: Lydia Form # ML14 Date: January 27, 2015 Reporting IH: Caoimhín P. Connell, Forensic IH Certification

Statement Signature I hereby certify that I conducted a preliminary assessment of the subject property in accordance with 6 CCR 1014-3, Part 1, § 4. I do hereby certify that the analytical results reported here are faithfully reproduced. In the section below, describe any variations from the standard: During the Preliminary Assessment, the field blanks were located in the tenth and 20th sample positions instead of the 11th and 21st, positions. Pursuant to the language required in 6 CCR 1014-3, § 8.8 I do hereby certify that I conducted clearance sampling of the subject property in accordance with 6 CCR 1014-3, Part 1, § 6. I further certify that the cleanup standards established by 6 CCR 1014-3, Part 1, § 7 have been met as evidenced by testing I conducted.

Signature Date: January 27, 2015

185 Bounty Hunter’s Lane, Bailey, Colorado 80421 Phone: 303-903-7494 www.forensic-applications.com

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Forensic Applications Consulting Technologies, Inc. Consultant Statement of Qualifications

FACTs project name: Lydia Form # ML15 January 27, 2015

Caoimhín P. Connell, has been involved in clandestine drug lab investigations since 2002 and meets the Colorado Revised Statute §24-30-1402 definition of an “Industrial Hygienist” and is authorized under 6 CCR 1014-3 to perform assessments in illegal drug laboratories. He has been a practicing Industrial Hygienist since 1987. Mr. Connell is a recognized authority in drug-lab operations and is a Certified Instructor in Meth-Lab Safety through the Colorado Regional Community Policing Institute, CRCPI (Colorado Division of Criminal Justice) and was the lead instructor for the CRCPI providing over 260 hours of methlab training for over 45 Colorado Law Enforcement Agencies, federal agents, probation and parole officers throughout Colorado judicial districts. He has provided meth-lab lectures to the US Air Force, the National Safety Council, and the American Industrial Hygiene Association (of which he is a member and serves on the Clandestine Drug Lab Work Group and for whom he conducted the May, 2010, Clandestine Drug Lab Course, and is a coauthor of the AIHA methlab assessment publication.) Mr. Connell is a member of the American Conference of Governmental Industrial Hygienists, the Occupational Hygiene Society of Ireland, the Colorado Drug Investigators Association, an appointed Member of the National Fire Protection Association, and the ASTM International Forensic Sciences Committee, (where he was the sole sponsor of the draft ASTM E50 Standard for the Assessment of Suspected Clandestine Drug Laboratories). From 2009, Mr. Connell served as the Industrial Hygiene Subject Matter Expert on the Federally funded Interagency Board (Health, Medical, and Responder Safety SubGroup), and was elected full member of the IAB-HMRS in 2011 where he now serves. He is the only private consulting Industrial Hygienist in Colorado certified by the Office of National Drug Control Policy High Intensity Drug Trafficking Area Clandestine Drug Lab Safety Program, and P.O.S.T. certified by the Colorado Department of Law. He has received over 194 hours of highly specialized law-enforcement sensitive training in drug lab operation, and under supervision of the US DEA, he has manufactured methamphetamine using a variety of street methods. He has received highly specialized drug lab assessment training through the Iowa National Guard, Midwest Counterdrug Training Center and the Florida National Guard Multijurisdictional Counterdrug Task Force, St. Petersburg College, Rocky Mountain HIDTA, as well as through the US NHTSA, and the U.S. Bureau of Justice Assistance (US Dept. of Justice) and he is currently ARIDE Certified. Mr. Connell is a current sworn law enforcement officer who has conducted clandestine laboratory investigations and performed risk, contamination, hazard and exposure assessments from both the law enforcement (criminal) perspective, and from the civil perspective in residences, apartments, motor vehicles, and condominia. Mr. Connell has conducted over 519 assessments of illegal drug labs in CO, SD, NE, OK, and collected over 4,840 samples during assessments (a partial detailed list of drug lab experience is available on the web at): http://forensic-applications.com/meth/DrugLabExperience2.pdf He has extensive experience performing assessments pursuant to the Colorado meth-lab regulation, 6 CCR 1014-3, and was an original team member on two of the legislative working-groups which wrote the original regulations for the State of Colorado and he was the primary contributing author of Appendix A (Sampling Methods And Procedures) and Attachment to Appendix A (Sampling Methods and Procedures Sampling Theory) of the original Colorado regulations. Mr. Connell strongly objected to the unscientific, unfounded and inappropriate amendments now applicable to those original regulations. Recommended by the US NIOSH as Peer Review Expert for the NIOSH 9109 Method, Methamphetamine, he has been admitted as a drug lab expert in Colorado, and an Industrial Hygiene Expert in Colorado in both civil and criminal courts as well as Federal Court in Pennsylvania. He has provided expert testimony in several criminal cases including Grand Jury testimony and testimony for US Bureau ATF and he testified before the Colorado Board of Health and Colorado Legislature Judicial Committee regarding methlab issues. Mr. Connell has provided services to private consumers, Indian Nations, Sate Investigators, and Federal Investigators.

185 Bounty Hunter’s Lane, Bailey, Colorado 80421 Phone: 303-903-7494 www.forensic-applications.com

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Post-Remediation Photograph Log Sheet FACTs project name: Lydia Form # ML9 Date: January 27 , 2015 Reporting IH: Caoimhín P. Connell, Forensic IH

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Post-Remediation Photograph Log Sheet FACTs project name: Lydia Form # ML9 Date: January 27 , 2015 Reporting IH: Caoimhín P. Connell, Forensic IH

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Post-Remediation Photograph Log Sheet FACTs project name: Lydia Form # ML9 Date: January 27 , 2015 Reporting IH: Caoimhín P. Connell, Forensic IH

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Appendix B Analytical Reports

Field Sampling Sheets

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Reservoirs Environmental, Inc. Reservoirs Environmental QA Manual

Effective January 1, 2014T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

PageCover Sheet 1Letter 2Report / Data 3Quality Control Data 4Chain of Custody 5

Forensic Applications

Final Report

RES 308448-1

December 31, 2014

P: 303-964-1986F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 1 of 4

1-866-RESI-ENVwww.reilab.com

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Reservoirs Environmental, Inc. Reservoirs Environmental QA Manual

Effective January 1, 2014T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

Laboratory Code: RESSubcontract Number: NALaboratory Report: RES 308448-1Project # / P.O. #: LydiaProject Description:

RES 308448-1

Sincerely,

Jeanne Spencer OrrPresident

Analyst(s): _____________________________________ Mike Schaumloeffel

December 31, 2014

Dear Customer,

Reservoirs has analyzed the following sample(s) using Gas Chromatography Mass Spectrometry (GC/MS) / GasChromatography Flame Ionization Detector (GC/FID) per your request. The analysis has been completed in generalaccordance with the appropriate methodology as stated in the analysis table. Results have been sent to your office.

property of the customer. Reservoirs Environmental, Inc. will not discuss any part of this study with personnel other thanthose authorized by the client. The results described in this report only apply to the samples analyzed. This report shallnot be reproduced except in full, without written approval from Reservoirs Environmental, Inc. Samples will be disposedof after sixty days unless longer storage is requested. If you should have any questions about this report, please feelfree to call me at 303-964-1986.

Reservoirs Environmental, Inc. is an analytical laboratory accredited for the analysis of Environmental matrices by theNational Environmental Laboratory Accreditation Program, Lab Certification #E871030. The laboratory is currentlyproficient in the in-house ERA PAT Program.

is the job number assigned to this study. This report is considered highly confidential and the sole

1809 Lydia Drive Lafayette, CO 80026

Caoimhin Connell

Bailey CO 80421

Forensic Applications185 Bounty Hunter Ln.

P: 303-964-1986F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 2 of 4

1-866-RESI-ENVwww.reilab.com

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Reservoirs Environmental, Inc. Reservoirs Environmental QA Manual

Effective January 1, 2014T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

RES Job Number:Client:Client Project Number / P.O.:Client Project Description:Date Samples Received:Analysis Type:Turnaround:Date Samples Analyzed:

Client Lab Reporting METHAMPHETAMINEID Number ID Number Limit CONCENTRATION

(µg) (µg)

LM122214-01 EM 1319463 0.05 4.62LM122214-02 EM 1319464 0.05 BRLLM122214-03 EM 1319465 0.05 BRLLM122214-04 EM 1319466 0.05 BRLLM122214-05 EM 1319467 0.05 BRLLM122214-06 EM 1319468 0.05 BRLLM122214-07 EM 1319469 0.05 44.75LM122214-08 EM 1319470 0.05 4.38LM122214-09 EM 1319471 0.05 0.96LM122214-10 EM 1319472 0.05 BRLLM122214-11 EM 1319473 0.05 BRLLM122214-12 EM 1319474 0.05 1.23LM122214-13 EM 1319475 0.05 1.17LM122214-14 EM 1319476 0.05 21.05LM122214-15 EM 1319477 0.05 0.92LM122214-16 EM 1319478 0.05 6.18LM122214-17 EM 1319479 0.05 2.57LM122214-18 EM 1319480 0.05 BRLLM122214-19 EM 1319481 0.05 0.67LM122214-20 EM 1319482 0.05 BRLLM122214-21 EM 1319483 0.05 4.75LM122214-22 EM 1319484 0.05 1.00LM122214-23 EM 1319485 0.05 0.67LM122214-24 EM 1319486 0.05 5.16LM122214-25 BX EM 1319487 0.05 BRL

December 23, 2014

5 DayMethamphetamine by GCMS

RESERVOIRS ENVIRONMENTAL, INC.NVLAP Accredited Laboratory #101896

AIHA Certificate of Accreditation #480 LAB ID 101533

TABLE I. ANALYSIS: METHAMPHETAMINE BY WIPE

* Unless otherwise noted all quality control samples performed within specifications established by the laboratory.

1809 Lydia Drive Lafayette, CO 80026

December 31, 2014

RES 308448-1

LydiaForensic Applications

P: 303-964-1986F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 3 of 4

DATA QA_________

1-866-RESI-ENVwww.reilab.com

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Reservoirs Environmental, Inc. Reservoirs Environmental QA Manual

Effective January 1, 2014T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

QUALITY CONTROL:

RES Job Number:Client:Client Project Number / P.O.:Client Project Description:Date Samples Received:Analysis Type:Turnaround:Date Samples Analyzed:

Matrix Matrix Duplicate Spike

(µg/100cm²) (µg/100cm²) (% RPD) (% Recovery) (% Recovery)

1 0.05 BRL 4 87 822 0.05 BRL 3 93 96

Quality Control Batch 1 = Samples LM122214-01 thru LM122214-08 (EM 1319463 thru 1319470).Quality Control Batch 2 = Samples LM122214-09 thru LM122214-25BK (EM 1319471 thru 1319487).

December 23, 2014

5 DayMethamphetamine by GCMS

* Unless otherwise noted all quality control samples performed within specifications established by the laboratory.

1809 Lydia Drive Lafayette, CO 80026

December 31, 2014

Quality Control Batch

RESERVOIRS ENVIRONMENTAL, INC.NVLAP Accredited Laboratory #101896

AIHA Certificate of Accreditation #480 LAB ID 101533

Laboratory Control SampleMatrix BlankReporting Limit

METHAMPHETAMINE BY WIPE

RES 308448-1

LydiaForensic Applications

P: 303-964-1986F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 4 of 4

DATA QA__________

1-866-RESI-ENVwww.reilab.com

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Reservoirs Environmental, Inc. Reservoirs Environmental QA Manual

Effective January 1, 2014T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

PageCover Sheet 1Letter 2Report / Data 3Quality Control Data 4Chain of Custody 5

Forensic Applications

Final Report

RES 310090-1

January 20, 2015

P: 303-964-1986F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 1 of 4

1-866-RESI-ENVwww.reilab.com

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Reservoirs Environmental, Inc. Reservoirs Environmental QA Manual

Effective January 1, 2014T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

Laboratory Code: RESSubcontract Number: NALaboratory Report: RES 310090-1Project # / P.O. #: LydiaProject Description:

RES 310090-1

Sincerely,

January 20, 2015

Dear Customer,

Reservoirs has analyzed the following sample(s) using Gas Chromatography Mass Spectrometry (GC/MS) / GasChromatography Flame Ionization Detector (GC/FID) per your request. The analysis has been completed in generalaccordance with the appropriate methodology as stated in the analysis table. Results have been sent to your office.

property of the customer. Reservoirs Environmental, Inc. will not discuss any part of this study with personnel other thanthose authorized by the client. The results described in this report only apply to the samples analyzed. This report shallnot be reproduced except in full, without written approval from Reservoirs Environmental, Inc. Samples will be disposedof after sixty days unless longer storage is requested. If you should have any questions about this report, please feelfree to call me at 303-964-1986.

Reservoirs Environmental, Inc. is an analytical laboratory accredited for the analysis of Environmental matrices by theNational Environmental Laboratory Accreditation Program, Lab Certification #E871030. The laboratory is currentlyproficient in the in-house ERA PAT Program.

is the job number assigned to this study. This report is considered highly confidential and the sole

1809 Lydia Dr., Lafayette CO 80026

Caoimhin Connell

Bailey CO 80421

Forensic Applications185 Bounty Hunter Ln.

Jeanne Spencer OrrPresident

Analyst(s): _____________________________________ Mike Schaumloeffel

P: 303-964-1986F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 2 of 4

1-866-RESI-ENVwww.reilab.com

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Reservoirs Environmental, Inc. Reservoirs Environmental QA Manual

Effective January 1, 2014T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

RES Job Number:Client:Client Project Number / P.O.:Client Project Description:Date Samples Received:Analysis Type:Turnaround:Date Samples Analyzed:

Client Lab Reporting METHAMPHETAMINEID Number ID Number Limit CONCENTRATION

(µg) (µg)

LM011415-01 EM 1331726 0.05 0.06LM011415-02 EM 1331727 0.05 BRLLM011415-03 EM 1331728 0.05 BRLLM011415-04 EM 1331729 0.05 BRLLM011415-05 EM 1331730 0.05 BRLLM011415-06 EM 1331731 0.05 0.08LM011415-07 EM 1331732 0.05 BRLLM011415-08 EM 1331733 0.05 BRLLM011415-09 EM 1331734 0.05 0.05LM011415-10 EM 1331735 0.05 BRLLM011415-11 BX EM 1331736 0.05 BRLLM011415-12 EM 1331737 0.05 BRLLM011415-13 EM 1331738 0.05 BRLLM011415-14 EM 1331739 0.05 0.22LM011415-15 EM 1331740 0.05 0.09LM011415-16 EM 1331741 0.05 BRLLM011415-17 EM 1331742 0.05 0.10LM011415-18 EM 1331743 0.05 BRLLM011415-19 BX EM 1331744 0.05 BRL

* Unless otherwise noted all quality control samples performed within specifications established by the laboratory.

1809 Lydia Dr., Lafayette CO 80026

January 20, 2015

RES 310090-1

LydiaForensic Applications

January 14, 2015

5 DayMethamphetamine by GCMS

RESERVOIRS ENVIRONMENTAL, INC.NVLAP Accredited Laboratory #101896

AIHA Certificate of Accreditation #480 LAB ID 101533

TABLE I. ANALYSIS: METHAMPHETAMINE BY WIPE

P: 303-964-1986F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 3 of 4

DATA QA_________

1-866-RESI-ENVwww.reilab.com

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Reservoirs Environmental, Inc. Reservoirs Environmental QA Manual

Effective January 1, 2014T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

QUALITY CONTROL:

RES Job Number:Client:Client Project Number / P.O.:Client Project Description:Date Samples Received:Analysis Type:Turnaround:Date Samples Analyzed:

Matrix Matrix Duplicate Spike

(µg/100cm²) (µg/100cm²) (% RPD) (% Recovery) (% Recovery)

1 0.05 BRL 8 104 117

1809 Lydia Dr., Lafayette CO 80026

January 20, 2015

Quality Control Batch

RESERVOIRS ENVIRONMENTAL, INC.NVLAP Accredited Laboratory #101896

AIHA Certificate of Accreditation #480 LAB ID 101533

Laboratory Control SampleMatrix BlankReporting Limit

METHAMPHETAMINE BY WIPE

RES 310090-1

LydiaForensic Applications

January 14, 2015

5 DayMethamphetamine by GCMS

* Unless otherwise noted all quality control samples performed within specifications established by the laboratory.

P: 303-964-1986F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 4 of 4

DATA QA__________

1-866-RESI-ENVwww.reilab.com

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Appendix C Contractor’s Submittals

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1809 Lydia Dr.Lafayette, CO

1/6/2015

Prepared for:

New Customer

Lance Smith

2971 Thunder Lake Cir.

Lafayette, CO 80026

720-309-3512

[email protected]

Prepared by:

BuildSafe Environmental Ltd.

CDPHE Registration No.: ACF - 19059

303 S Broadway Unit 200-239

Denver, CO. 80209

[email protected]

303 522 4315

LIMITED ASBESTOS INSPECTION REPORT

303 S Broadway, 200-239, Denver CO 80209 www.BuildSafeEnviro.com

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Section 1 Inspection Project Summary

1.1 Photo Log of Asbestos Containing Materials (if identified)

1.2 Summary of Asbestos Samples

Section 2 Results and Recommendations

Section 3 Project Overview

Section 4 Asbestos Inspection Procedure

4.1 Suspect Asbestos Containing Building Materials

4.2 Sampling and Laboratory Analysis

Section 5 Conclusion

5.1 Limitations

Appendix

A - Laboratory Report and Chain of Custody Form

List of Acronyms

ACM Asbestos Containing Materials BBA Baseboard Adhesive

CA Carpet Adhesive

G Good CDW Composite Drywall

D Damaged CMS CMU Sealant

SD Significantly Damaged CT Ceiling Tile

DT Duct Tape/Wrap

F Friable DW Drywall

NFI Non-Friable Category I FTM Floor Tile Mastic

NFII Non-Friable Category II MA Miscellaneous Adhesive

MS Miscellaneous Sealant

NA Not Analyzed OT Other Material

ND None Detected PI Pipe Insulation

PL Plaster

EA Each RSG Roof Shingle

LF Linear Feet RSH Roof Sheeting

SF Square Feet RSL Roofing Sealant

SVF Sheet Vinyl Flooring

Trace ≤1% by (Point Count/Composite) TS Textured Surfacing

ACM ACM (>1% asbestos) WG Window Glazing

Table of Contents

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Job ID: 150105-5 Site Address: 1809 Lydia Dr.

Date: 01/05/15 Lafayette, CO

Inspector: Customer: Lance Smith

CO. Cert #: 17817 Client: New Customer

Owner/Site Contact: Lock Box

Property Type: SFR

Appx Age: N/A

Laboratory: Reason:

NVLAP #: Affected Area:

Results Time: Rush

# of Samples: 11 Inspector Notes:

Inspection Type:

Homogenous Areas in Work Scope Table

# Class/ID Samples Functional Space Scope Qty

1 TS 5 Throughout 1150 SF

2 CDW 1 Throughout 300 SF

3 TS 3 Up NW bedroom 450 SF

4 CDW 1 Up NW bedroom 100 SF

5 CDW 1 Garage 100 SF

6

7

8

9

10

LTD Renovation ACM AHERA/Reg 8

Investigative

Popcorn ceiling, painted drywall in

bedroom, garage

Meth cleanup, test materials which

must be removed

1.1 Photo Log of Asbestos Containing Materials (if identified)None of the materials sampled contain asbestos.

Section 1 Inspection Project Summary

Blake Weise

101-896-0

Reservoirs

TJC on unfinished drywall

Description

White popcorn ceiling

TJC w/ white popcorn

White spray texture on DW

TJC w/ white spray texture

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Mat'l

ID # Cond. Category Result

TS 1-1 1 G F ND

TS 1-2 1 G F ND

TS 1-3 1 G F ND

TS 1-4 1 G F ND

TS 1-5 1 G F ND

CDW 1-1 2 G NFII ND

TS 2-1 3 G F ND

TS 2-2 3 G F ND

TS 2-3 3 G F ND

CDW 2-1 4 G NFII ND

CDW 3-1 5 G NFII ND

Section 2 Results and Recommendations

No asbestos-containing building materials have been identified within the affected area(s) of the Site

Address. Please work safely and if any additional materials are discovered that are not listed in the

“Homogenous Areas in Work Scope” table, please contact BuildSafe prior to disturbing these materials.

Any work performed on asbestos-containing building materials and/or trace asbestos-containing building

materials is subject to OSHA regulations, including but not limited to: hazard communication, asbestos

construction industry, general construction industry, and respiratory protection standards. Worker exposure

assessments are part of the asbestos construction industry standard and include excursion limits and 8-hour

time-weighted permissible exposure limits which, if exceeded, may require additional engineering or

administrative controls to properly protect workers engaged in activities that may damage or disturb

materials which contain asbestos.

Garage, N wall, NW corner, 5ft

Upstairs, NW bedroom, E wall, 2ft N, 3ft

Upstairs, NW bedroom, N wall, E of window, 5ft

Upstairs, NW bedroom, closet, SE corner, 2ft

1.2 Summary of Asbestos Samples

Sample Locations

Bulk Sample and Locations Table

Main level, living room, ceiling, 4ft N, 6ft W

Main level, living room, ceiling, 8ft N, 8ft W

Upstairs, S bedroom. Ceiling, 4ft S, 5ft W

Upstairs, hallway, E of attic hatch, 1ft N

Upstairs, NW bedroom, 2ft E, 3ft N

Upstairs, NE bedroom, E ceiling corner, 3ft S

Upstairs, NW bedroom, W wall, 2ft S, 7ft

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Section 3 Project Overview BuildSafe Environmental, Ltd. (BuildSafe) was contracted by the client to perform a

limited repair/renovation specific asbestos inspection (inspection) at the above referenced

“Site Address”. The inspection was conducted by an Environmental Protection Agency

(EPA) accredited and Colorado Department of Public Health and Environment (CDPHE)

certified Asbestos Building Inspector. The inspection was performed at the direction of

the client and only includes those materials, locations, and quantities specified in the

“Homogenous Areas in Work Scope Table”.

The client is planning repair/renovation activities that will disturb suspect Asbestos

Containing Building Materials (ACBM) within the repair/renovation affected areas at the

Site Address. CDPHE Air Quality Control Commission Regulation No. 8, Part B – Asbestos

(Reg 8) requires that all suspect ACBMs be properly inspected and sampled by certified

personnel prior to conducting any repair/renovation activities that will disturb the suspect

ACBMs. All samples were analyzed by a laboratory accredited under the National

Voluntary Laboratory Accreditation Program (NVLAP). The CDHPE has established the

following trigger levels for different types of properties, which specify how suspect and

confirmed ACBMs are inspected and subsequently abated:

With regard to single-family residential dwellings (SFRD), the trigger levels are

50 LF on pipes, 32 SF on other surfaces, or the volume equivalent of a 55-gallon

drum

With regard to all areas other than SFRDs, the trigger levels are 260 LF on pipes,

160 SF on other surfaces, or the volume equivalent of a 55-gallon drum

The purpose of the inspection was to identify, visually inspect, and sample all suspect

ACBMs, at the direction of the client, which may be disturbed during the course of the

repair/renovation work.

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Section 4 Asbestos Inspection Procedure

The inspection procedure was conducted in accordance with EPA Asbestos Hazard and

Emergency Response Act (AHERA), CDPHE Reg 8, and applicable Occupational Safety

and Health Administration (OSHA) guidelines and regulations. These regulations specify

requirements and protocols for conducting asbestos inspections, sample analysis, and

asbestos abatement.

4.1 Suspect Asbestos Containing Building Materials

Homogenous Material Types

The inspection involved identification and sampling of suspect ACBMs in the areas

established by the client that would be part of the scope of work. Suspect ACBMs were

grouped into homogenous materials based on color, texture, and date of application.

Homogenous materials were given distinct codes (CDW01, FTC02, TS05, etc.) based on

the type sequence of the homogenous material. Details about the size, color, condition,

friability, quantity, location within each functional space and other important details for

each homogenous material were reported as part of the inspection. Homogenous

materials are grouped into one of three categories based on intended use:

1. Surfacing Material – material that is sprayed on, troweled on, or otherwise

applied to surfaces, such as acoustical plaster on ceilings and fireproofing materials

on structural members, or other materials on surfaces for acoustical, fireproofing,

or other purposes.

2. Thermal System Insulation – material applied to pipes, fittings, boilers,

breeching, tanks, ducts, or other interior structural components to prevent heat

loss or gain, or water condensation, or for other purposes.

3. Miscellaneous Materials – interior building material on structural components,

structural members or fixtures, such as floor and ceiling tiles, and does not include

surfacing material or thermal system insulation.

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Homogenous Material Friability

Each homogenous material was given one of the three following friability categories

defined by the EPA and CDPHE:

1. Friable Material – materials that can be crumbled or reduced to powder by hand

pressure.

2. Category I Non-friable Material – materials that cannot be crumbled or

reduced to powder by hand pressure including resilient floor coverings, gaskets,

packing materials and asphalt impregnated roofing materials.

3. Category II Non-friable Materials – all other materials that cannot be

crumbled or reduced to powder by hand pressure that do not include category I

non-friable materials.

Homogenous Material Condition

Each homogenous material was given one of three condition categories based on visual

observation defined by the EPA and CDPHE:

1. Good Condition – No visible signs of damage were observed during the

inspection.

2. Damaged Condition – Visible signs of damage less than ten percent spread over

the entire material or twenty five percent localized.

3. Significantly Damaged Condition – Severe damage greater than ten percent

spread over the entire material or twenty five percent localized.

4.2 Sampling and Laboratory Analysis

Sample Collection

Bulk samples of each suspect homogenous material were collected randomly throughout

the homogenous material area within the scope of work. Bulk samples were sampled all

of the way through the material so that all associated layers within each homogenous

material are represented. Bulk samples were placed in closeable sample bags and then

labeled with a permanent marker with distinct sample identifiers (e.g., CDW1-1, FTC2-1,

MISC2-3, etc.) for transport to the laboratory. Sample locations and photographs of the

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homogenous materials were also collected at this time during the inspection. Sample

quantities of each homogenous material were collected based on material type and

quantity detailed in the following table as required by regulation:

Homogenous Material

Type Quantity

Minimum Number of

Samples

Surfacing material

0 to <1,000 SF

1,000 to 5,000 SF

>5,000 SF

3

5

7

Thermal System Insulation Each Material

Patch < 6 LF, SF

3

1

Miscellaneous Material Each Material 1

Laboratory Sample Analysis

Bulk samples were submitted to the laboratory along with a completed chain of custody

form to the above listed NVLAP accredited laboratory for analysis by polarized light

microscopy (PLM) techniques per EPA methodology (EPA-600/M4-82-020, Dec. 1982).

Microscopic visual estimation was used in obtaining the percentage of asbestos within

each layer of the bulk samples.

Asbestos Containing Building Materials

EPA and CDPHE both define an asbestos containing building material (ACBM) as a

material which has an asbestos content of greater than one percent. In the event that a

friable material is estimated to contain “trace” or between zero-to-one percent, that

material must undergo a point-count analysis by the laboratory to confirm that the

material is trace asbestos-containing. Further, if a point count analysis is performed on a

bulk sample, the point count result takes precedence over the visual estimation result.

See appendix A for laboratory report and chain of custody documents.

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Section 5

Conclusion

BuildSafe has performed a limited repair/renovation specific asbestos inspection of the

home/facility located at the Site Address. Through visual inspection and laboratory

analysis of bulk samples collected at the Site Address, BuildSafe recommends hiring a

certified general asbestos abatement contractor to remove any ACBMs that may have

been identified within the scope of work. All inspection activities were conducted at the

direction of the client and only include those materials, quantities and locations detailed

in sections 1 and 2 of this report. See sections 1 and 2 of this report for information

regarding inspection scope of work, suspect ACBMs, confirmed ACBMs, sample

information and laboratory analysis results.

5.1 Limitations

General Comments and Limitations

Reasonable effort was made by BuildSafe to locate and sample accessible suspect ACBMs

within the scope of work. However, for any structure, the existence of unique or

concealed suspect ACBMs is a strong possibility. BuildSafe only inspected and collected

suspect ACBM bulk samples in the repair/renovation areas at the direction of the client.

This limited repair/renovation asbestos inspection report is not considered a

comprehensive asbestos inspection report and is only valid for the materials and locations

detailed in sections 1 and 2 of this report.

Should further repair/renovation work expand outside of materials and locations listed in

sections 1 and 2 of this report, those locations must be properly inspected and sampled

by qualified personnel prior to disturbance of suspect ACBMs. Any subsequent abatement

of ACBMs must be performed in accordance with all federal, state and local regulations

pertaining to abatement, transport, and disposal of ACBMs.

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The asbestos inspection was conducted in a manner consistent with the level of care and

skill exercised by professionals of the asbestos inspection profession. The results,

findings, conclusions and recommendations expressed in this report are based on

conditions observed during our limited inspection of the repair/renovation areas. The

information contained in this report is relevant to the date on which this survey was

performed, and should not be relied upon to represent conditions at a later date. This

report has been prepared on behalf of and exclusively for use by the client for specific

application to the project as discussed. Contractors or consultants reviewing this report

must draw their own conclusions regarding further investigation or remediation deemed

necessary. BuildSafe does not warrant the work of regulatory agencies, laboratories or

other third-parties supplying information which may have been used in the preparation

of this report. No warranty, express or implied is made.

Sincerely,

Blake Weise

BuildSafe Environmental, LTD

303 S Broadway, Unit 200-239

Denver, CO 80209

970.389.5572

[email protected]

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Appendix A Laboratory Report and Chain Of Custody Form

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Reservoirs Environmental, Inc.

Reservoirs Environmental QA Manual

Effective January 1, 2014

T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

Subcontract Number: NA

Laboratory Report: RES 309137-1

Project # / P.O. # 150105-5

Project Description: 1809 Lydia Dr. Lafayette, CO

RES 309137-1

Sincerely,

is the job number assigned to this study. This report is considered highly confidential

and the sole property of the customer. Reservoirs Environmental, Inc. will not discuss any part of this study with

personnel other than those of the client. The results described in this report only apply to the samples analyzed.

This report must not be used to claim endorsement of products or analytical results by NVLAP or any agency of the

U.S. Government. This report shall not be reproduced except in full, without written approval from Reservoirs

Environmental, Inc. Samples will be disposed of after sixty days unless longer storage is requested. If you have any

questions about this report, please feel free to call 303-964-1986.

Jeanne Spencer

President

January 5, 2015

Dear Customer,

Reservoirs Environmental, Inc. is an analytical laboratory accredited for the analysis of Industrial Hygiene and

Environmental matrices by the National Voluntary Laboratory Accreditation Program (NVLAP), Lab Code 101896-0

for Transmission Electron Microscopy (TEM) and Polarized Light Microscopy (PLM) analysis and the American

Industrial Hygiene Association (AIHA), Lab ID 101533 - Accreditation Certificate #480 for Phase Contrast

Microscopy (PCM) analysis. This laboratory is currently proficient in both Proficiency Testing and PAT programs

respectively.

Reservoirs Environmental, Inc. has analyzed the following samples for asbestos content as per your request. The

analysis has been completed in general accordance with the appropriate methodology as stated in the attached

analysis table. The results have been submitted to your office.

Build Safe Environmental

303 S. Broadway #200-239

Denver CO 80209

Blake Weise

P: 303-964-1986

F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 1 of 4

1-866-RESI-ENV

www.reilab.com

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Reservoirs Environmental, Inc.

Reservoirs Environmental QA Manual

Effective January 1, 2014

T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

TABLE PLM BULK ANALYSIS, PERCENTAGE COMPOSITION BY VOLUME

RES Job Number:

Client:

Client Project Number / P.O.:

Client Project Description:

Date Samples Received:

Method: ND=None Detected

Turnaround: TR=Trace, <1% Visual Estimate

Date Analyzed: Trem-Act=Tremolite-Actinolite

Client Non Non-Sample Sub Asbestos FibrousNumber Physical Part Fibrous Components

Description (%) Mineral Visual Components (%)Estimate (%) (%)

TS1-1 EM 1324105 A

B

White texture w/ white paint

White tan drywall

50

50ND

ND

TR

50

100

50

TS1-2 EM 1324106 A

B

C

White compound

White texture w/ white paint

Tan/white drywall

20

38

42

ND

ND

ND

0

1

70

100

99

30

TS1-3 EM 1324107 A

B

White texture w/ white paint

Tan white drywall

46

54ND

ND

TR

65

100

35

TS1-4 EM 1324108 A

B

Tan/white drywall

White texture w/ white paint

40

60ND

ND

60

TR

40

100

TS1-5 EM 1324109 A

B

White texture w/ white paint

White drywall

25

75ND

ND

TR

20

100

80

RESERVOIRS ENVIRONMENTAL, INC.NVLAP Lab Code 101896-0

TDH Licensed Laboratory # 30-0136

ID Number

L

A

Y

E

R

Lab

2 Hour

RES 309137-1

150105-5

Build Safe Environmental

Asbestos Content

January 5, 2015

1809 Lydia Dr. Lafayette, CO

EPA 600/R-93/116 - Short, Bulk

January 5, 2015

P: 303-964-1986

F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 2 of 4

1-866-RESI-ENV

www.reilab.com

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Reservoirs Environmental, Inc.

Reservoirs Environmental QA Manual

Effective January 1, 2014

T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

TABLE PLM BULK ANALYSIS, PERCENTAGE COMPOSITION BY VOLUME

RES Job Number:

Client:

Client Project Number / P.O.:

Client Project Description:

Date Samples Received:

Method: ND=None Detected

Turnaround: TR=Trace, <1% Visual Estimate

Date Analyzed: Trem-Act=Tremolite-Actinolite

Client Non Non-Sample Sub Asbestos FibrousNumber Physical Part Fibrous Components

Description (%) Mineral Visual Components (%)Estimate (%) (%)

RESERVOIRS ENVIRONMENTAL, INC.NVLAP Lab Code 101896-0

TDH Licensed Laboratory # 30-0136

ID Number

L

A

Y

E

R

Lab

2 Hour

RES 309137-1

150105-5

Build Safe Environmental

Asbestos Content

January 5, 2015

1809 Lydia Dr. Lafayette, CO

EPA 600/R-93/116 - Short, Bulk

January 5, 2015

CDW1-1 EM 1324110 A

B

C

D

White joint compound joint compound

White tape

White texture w/ white paint

White drywall

2

3

10

85

ND

ND

ND

ND

TR

90

0

18

100

10

100

82

TS2-1 EM 1324111 A

B

White/multi-layered paint w/ white texture

White drywall

30

70ND

ND

0

50

100

50

TS2-2 EM 1324112 A

B

White/multi-layered paint w/ white texture

Tan/white drywall

35

65ND

ND

0

70

100

30

P: 303-964-1986

F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 3 of 4

1-866-RESI-ENV

www.reilab.com

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Reservoirs Environmental, Inc.

Reservoirs Environmental QA Manual

Effective January 1, 2014

T:\QAQC\Lab\Reservoirs Environmental QA Manual.doc

TABLE PLM BULK ANALYSIS, PERCENTAGE COMPOSITION BY VOLUME

RES Job Number:

Client:

Client Project Number / P.O.:

Client Project Description:

Date Samples Received:

Method: ND=None Detected

Turnaround: TR=Trace, <1% Visual Estimate

Date Analyzed: Trem-Act=Tremolite-Actinolite

Client Non Non-Sample Sub Asbestos FibrousNumber Physical Part Fibrous Components

Description (%) Mineral Visual Components (%)Estimate (%) (%)

RESERVOIRS ENVIRONMENTAL, INC.NVLAP Lab Code 101896-0

TDH Licensed Laboratory # 30-0136

ID Number

L

A

Y

E

R

Lab

2 Hour

RES 309137-1

150105-5

Build Safe Environmental

Asbestos Content

January 5, 2015

1809 Lydia Dr. Lafayette, CO

EPA 600/R-93/116 - Short, Bulk

January 5, 2015

TS2-3 EM 1324113 A

B

White/multi-layered paint w/ white texture

White/tan drywall

38

62ND

ND

0

60

100

40

CDW2-1 EM 1324114 A

B

C

D

White/multi-layered paint w/ white texture

White tape

White joint compound

White drywall

4

4

4

88

ND

ND

ND

ND

0

85

TR

20

100

15

100

80

CDW3-1 EM 1324115 A

B

C

D

White white compound

White tape

White joint compound

White drywall

1

2

2

95

ND

ND

ND

ND

2

85

0

10

98

15

100

90

TEM Analysis recommended for organically bound material (i.e. floor tile) if PLM results are <1%.

Analyzed by: Data QA:

P: 303-964-1986

F: 303-477-4275

5801 Logan Street, Suite 100 Denver, CO 80216

Page 4 of 4

1-866-RESI-ENV

www.reilab.com

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Appendix D Compact Digital Disc