ATTACHMENT 06 - XGFG182009 F-35 Alter B400 AMXS - Asbestos LBP Hazmat Assessment.pdf

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December 18, 2020

Gene O. Brown, P.E.

Principal, Director of Federal Programs Frankfurt-Short-Bruza Associates, P.C. (FSB) Oklahoma City, OK 73118

Re: Asbestos, Lead-bearing Paint, and Hazardous Materials Assessment XGFG182009 – F35: Building B400 W50S9F20F0002 Truax Field Madison, WI 53704

Mr. Brown:

On behalf of Frankfurt-Short-Bruza Associates (FSB), Ayres Associates (Ayres) assessed Building B400 at Truax Field for the presence of asbestos-containing materials (ACM), lead-bearing paint (LBP), and hazardous materials. The two-story building encompasses approximately 63,617 square feet and is used as an aircraft maintenance hangar. The building was constructed in 1994. It is our understanding that the building may be renovated. This assessment's goal was to identify ACM, LBP, or other hazardous materials before renovation for estimating costs. Appendix A contains a figure showing the site location and a figure showing the floor plan of Building B400.

Asbestos Assessment The Wisconsin Department of Natural Resources (WDNR) requires building owners or operators to inspect for the presence of ACM before renovation or demolition. ACM refers to any building material containing greater than 1% asbestos. In all cases, materials may be assumed to contain asbestos but can never be assumed not to contain asbestos. If a material is assumed to contain asbestos, then it must be appropriately managed as ACM. Any suspect ACM that is not listed in this report should be sampled or assumed to contain asbestos.

Asbestos-containing materials, as designated by the WDNR, are defined as:

Category I non-friable ACM means asbestos-containing packings, gaskets, resilient floor coverings, and asphalt roofing products that contain more than 1% asbestos. When dry, category I non-friable ACM does not crumble, pulverize, or reduce to powder under hand pressure. These materials can remain in place during demolition or renovation if they are not in poor condition and are not rendered friable by handling, transporting, or disposal. Construction and demolition (C&D) material containing non-friable category I ACM may be disposed of at an approved C&D landfill, including a WDNR-approved one-time disposal landfill, or at any other landfill with a plan of operation approved under chapter 289, Stats. Contact the landfill for assistance. However, non-friable ACM that is sanded, ground, cut, or abraded during the renovation should be treated as friable ACM and disposed of accordingly.

Category II non-friable ACM means any non-friable material, excluding category I non-friable ACM, containing more than 1% asbestos. When dry, category II non-friable ACM does not crumble, pulverize, or reduce to powder under hand pressure. An asbestos inspector classifies materials as category II non-friable ACM on a case-by-case basis. The WDNR requires the removal of category II non-friable ACM that is likely to become friable during demolition or renovation. Cement board and transite are examples of category II non-friable ACM that often become friable and should be removed before demolition or renovation.

Gene O. Brown, P.E December 18, 2020

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Regulated ACM (RACM) means friable ACM and category I non-friable ACM that has become friable or that is subjected to sanding, grinding, cutting, or abrading. RACM also includes category II non-friable ACM that is likely to become friable during demolition. Materials such as pipe insulation, duct paper wrap, sprayed on, or tiled sound insulation materials are usually considered RACM. Friable ACM has little structural strength and readily releases asbestos fibers upon breaking. The WDNR requires the removal of RACM before demolition or renovation.

Methodology On October 13, 2020, William Honea (AII-226200, exp. 12/16/2020) and Thomas Gaieck (AII-256096, exp. 11/16/2021) of Ayres, Wisconsin-certified asbestos inspectors, sampled building materials for laboratory analysis. The methods used to identify suspect materials, collect samples, analyze materials generally follow EPA, 40 CFR 763, and other applicable federal and state regulations and guidelines. At the time of this assessment, the property was occupied and in use. Ayres used limited destructive sampling methods to prevent exposing workers to fiber releases and avoid damage to operational equipment and critical building components. Copies of their current inspector cards are in Attachment B.

This assessment's scope included estimating the quantities of reasonably and safely accessible ACM, sampling suspect materials, and summarizing their physical condition. The condition of ACM is essential for determining if it must be removed before renovation or demolition or if it can remain in place and be removed as asbestos-containing debris.

Samples of suspect materials were submitted to EMSL Analytical in Minneapolis, Minnesota, for analysis by polarized light microscopy (PLM) using EPA method 600/R-93/116. National Emission Standards for Hazardous Air Pollutants (NESHAP) requires the verification of PLM results of less than 10% by point-counting, or those materials must be assumed and treated as ACM. In this assessment, all samples with PLM results greater than 1% were considered ACM, and no samples required verification by point-counting. The appropriate chain-of-custody forms accompanied the samples submitted for laboratory analysis.

This report is only intended to identify the location, condition, and estimated quantity of ACM, not to require specific response actions by the contractor. A certified asbestos inspector should test suspect ACM found during demolition that is not described in this report.

Asbestos Results A summary of the quantities, locations, conditions of sampled materials are provided in the tables below.

Attachment C contains a laboratory report and chain-of-custody. Attachment D contains an asbestos sample summary table, which documents the materials sampled and the locations where samples were collected.

Asbestos-containing materials were not confirmed to be present in the building through testing. However, a previous asbestos inspection conducted by the Air National Guard Technical Services Center's Asbestos Management Team in June 2006 identified transite panels in the hangar bay on the northwest corner at the bottom of the door, which contained 25% chrysotile. Transite panels along the main door on the north side of the bay are considered ACM. At the time of Ayres Associates' assessment, the area along the main door was inaccessible, and the presence of these transite panels could not be confirmed.

If present, these transite panels are considered non-friable Category II ACM. A copy of pertinent sections of the 2006 report regarding the transite panels is included in Attachment D.

The following materials are assumed or previously confirmed to contain asbestos and are considered non-friable category I or category II ACM:

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Non-friable Category I and Category II ACM

Material Locations Quantity Positive Samples Asbestos Content

Electrical Panels Throughout Building 300 SF NA Assumed Roofing Materials Roof 43,250 SF NA Assumed

Fire Door Rm 206 1 ea (20 SF) NA Assumed Transite Panels Main Door on North Side of Bay 4,125 SF Yes 25% Chrysotile

Notes: The quantities of materials were estimated based on observations made in October 2020. Remove non-friable ACM before recycling any attached substrates, such as wood, metal, glass, concrete, or other masonry materials. See Attachment D for sample locations and test results. A total of 22 electrical/control panels were identified during the site visit.

Limitations The quantities of ACM listed in this report are visual estimates, not exact measurements. Additionally, ACM classifications are based on condition and may change as the condition of building materials change.

Ayres does not sample active mechanical or electrical systems unless they are de-energized by certified personnel following lockout/tag-out procedures. To maintain safe working conditions and the integrity of these building systems, their components were not sampled and were assumed to contain asbestos.

Likewise, destructive testing was limited in some areas to maintain the integrity of critical structural components, such as the roof system and walls. Additional destructive sampling and wall cavity investigation may be necessary if these areas will be disturbed during demolition or renovation. Similarly, because this was an active facility, Ayres did not assess ACM's presence in operational equipment.

Asbestos Recommendations A certified asbestos company should abate RACM and non-friable ACM that is likely to become friable before starting demolition or renovation activities that are likely to disturb them. Similarly, ACM should be abated before recycling any attached substrates, such as wood, metal, glass, concrete, or other masonry materials. The selected asbestos company should be licensed to perform abatement work in Wisconsin by the Wisconsin Department of Health Services (DHS). Before beginning any demolition or activities involving the disturbance of ACM, submit a "Notification of Demolition and Renovation and Application for Permit Exemption" form and applicable fees to the WDNR (Attachment E).

The quantities of RACM and non-friable ACM listed in this report are visual estimates. Ayres recommends verifying these amounts before project design, bidding, budgeting, or submitting a notification of demolition activities to WDNR.

Any suspect ACM found during demolition or renovation not described in this report should either be sampled by a certified asbestos inspector and analyzed; or assumed to contain asbestos. Manage confirmed and assumed ACM following all applicable federal, state, and local regulatory requirements.

Several WDNR publications are available to guide building owners and operators through the proper handling and disposal procedures for ACM (Attachment E).

Lead-bearing Paint Assessment Ayres assessed the presence of lead-bearing paint on masonry and metal surfaces. Testing was completed to assist with the removal and recycling of these materials. Any paint that was not sampled should be assumed to contain lead until additional testing proves otherwise.

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Paint samples were analyzed by Flame Atomic Absorption Spectroscopy (SW 846 5050B/7000B), and the lead concentrations were reported as percent by weight. This method analyzes the sample as a whole and does not identify the lead content in discrete paint layers. Paint is considered lead-bearing paint in Section 254.11(8) of Wisconsin Statues if it contains more than 0.5% by weight or 1.0 milligrams per square centimeter (mg/cm2).

Lead-bearing Paint Results A total of ten paint samples were collected from interior masonry and metal surfaces. Three of the samples contained lead at a concentration above the LBP threshold of 0.5% by weight. These samples were collected in Room 205. The white paint on the concrete block (3.9% wt) in the storage room and the gray (6.5% wt) and tan (26% wt) paint on the metal roof beams were detected above the LBP threshold.

Five additional samples also contained detectable concentrations of lead at concentrations below the LBP threshold. Analytical results for the paints tested are summarized in Attachment F. The laboratory report is included in Attachment G.

Lead Bearing Paint Greater than 0.5%wt

Color Substrate Location Quantity Concentration White Concrete Wall Interior side of exterior walls 18,000 SF 3.9% wt

Gray Metal Roof Deck and Beams

Underside of flat roof deck and on supporting beams 20,000 SF 6.5% wt

Tan Metal Roof Deck and Beams

Underside of flat roof deck and on supporting beams 20,000 SF 26% wt

Lead-bearing Paint Recommendations If the concrete block and roof beams identified above are removed during renovation activities, they must be disposed of in a construction and demolition landfill or a municipal solid waste landfill licensed by the WDNR. The painted concrete block can also be crushed and recycled if the material is used as structural fill beneath an impermeable material such as a building foundation or parking lot, with a Low Hazard Waste Exemption for Reuse of Concrete Coated with Lead-bearing Paint approved by the WDNR. The concrete block and metal roof beams can be recycled If the lead-bearing paint is first abated by state-certified abatement workers. If the paint is abated, additional testing may be required to determine whether the remediation waste generated by the abatement is classified as hazardous waste under NR 661, Wisconsin Administrative Code.

Hazardous Materials Survey During the assessment, Ayres noted other hazardous or environmentally harmful materials that may require specialized disposal. Hazardous materials such as lead, mercury, chlorofluorocarbons (CFCs), hydrofluorocarbons (HCFCs), and polychlorinated biphenyls (PCBs) are often found in air conditioners, lightbulbs, light ballasts, thermostats, and appliances that are components of the building. Items containing hazardous materials should be removed before demolition and disposed of following applicable state and federal regulations. Attachment H contains a summary of building components that potentially contain hazardous materials. See WDNR publication in Attachment E for information regarding the management of these materials.

This report is intended for the sole use of the FSB. Ayres does not assume liability for the use of this report by unauthorized parties, nor does Ayres assume responsibility or liability for the discovery or

608.443.1200 | 5201 E. Terrace Drive, Suite 200 | Madison, WI 53718 www.AyresAssociates.com

Project: 51-0243.20 File: \\ayres\_Active\51\MD\00-51-0467 WIANG_Bed Down Project\Additional Truax Sites Project\Asbestos Reports\Building 400\400 Asbestos Report.docx elimination of adverse environmental conditions that could cause accidents, injury, damage, or otherwise create a hazardous environment.

Please do not hesitate to contact me with questions or concerns at 608-443-1292 or Jeff Steiner at 608.443.1259.

Sincerely, Ayres Associates, Inc

Thomas P. Gaieck Jeffrey C. Steiner, PG, PH, CPG Certified Asbestos Inspector AII-256096 Senior Hydrogeologist/Project Manager Direct: 608.443.1292 Direct: 608.443.1259 GaieckT@AyresAssociates.com SteinerJ@AyresAssociates.com

TPG:ac

Enclosure

Attachment A – Figures

Attachment B – Asbestos Inspector Credentials

Attachment C – Asbestos Laboratory Reports and Chain-of-Custody

Attachment D – Asbestos Sample Summary Table and ANG Report

Attachment E – WDNR Form 4500-113, WDNR Asbestos Publications, and Information on Identifying, Handling, and Properly Disposing of Hazardous Materials (WDNR Guidance WA-651)

Attachment F – Paint Sample Summary Table

Attachment G –Paint Laboratory Report and Chain-of-Custody

Attachment H – Hazardous Material Summary Table

Attachment A

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Asbestos Inspector Credentials

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Asbestos Laboratory Reports and Chain-of-Custody

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Asbestos Sample Summary Table

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Bl ue

/N on

-F ib ro us

N on e D et ec te d

A

M as tic Bl ue la m in at e flo or in g w ith m as tic 2n d Le ve l s ta ir la nd in g

C Ta n/ N on -F ib ro us N on e

D et ec te d

A Le ve le r Bl ue la m in at e flo or in g w ith m as tic 2n d Le ve l s ta ir la nd in g

C G ra y/

N on

-F ib ro us

N on e D et ec te d

A

C au lk C au lk a ro un d pi pe c ha se 2n d Le ve l h al l C

W hi te /N on -F ib ro us N on e

D et ec te d

A C ei lin g Ti le 2'

X2 ' C ei lin g Ti le R m

G ra y/

Fi br ou s

N on e D et ec te d

A

U nd er co at U nd er co at u nd er s in k

R m

Bl ac k/ N on -F ib ro us N on e

D et ec te d

A C au lk

C au lk u nd er s in k R m

Be ig e/

N on

-F ib ro us

N on e D et ec te d

A

Vi ny l w al l b oa rd Vi ny l w al l b oa rd

R m

G ra y/ W hi te

/F ib ro us

N on e D et ec te d

A

Fl oo rin g

La m in at e flo or w ith m as tic

R m

A &B

G ra y/ N on -F ib ro us N on e

D et ec te d

A M as tic

La m in at e flo or w ith m as tic

R m

A &B

Ta n/

N on

-F ib ro us

N on e D et ec te d

A

Le ve le r

La m in at e flo or w ith m as tic

R m

A &B

G ra y/ N on -F ib ro us N on e

D et ec te d

A W ra p

AC

d uc t i ns ul at io n on s qu ar e du ct

1s t l ev el la nd in g

St ai r B Ta

/W hi te /S ilv er

/F ib ro us

N on e D et ec te d

A

In su la tio n

AC

d uc t i ns ul at io n on s qu ar e du ct 1s t l ev el la nd in g St ai r B

Ye llo w /N on -F ib ro us N on e

D et ec te d

A W ra p

In su la tio n on ro un d

AC

d uc t St ai r l an di ng B

Ta n/

W hi te /S ilv er

/F ib ro us

N on e D et ec te d

A

In su la tio n In su la tio n on ro un d

AC

d uc t

St ai r l an di ng

B Ye llo w

/F ib ro us

N on e D et ec te d

A

M as tic In su la tio n in w ire c ha se

St ai r l an di ng

B G ra y/

W hi te /N on -F ib ro us N on e

D et ec te d

A In su la tio n

In su la tio n in w ire c ha se St ai r l an di ng B

Ye llo w /F ib ro us N on e

D et ec te d

A W ra p

3" P ip e in su la tio n w ra p

St ai r l an di ng

B Ta n/ W hi te

/S ilv er /N on -F ib ro us N on e

D et ec te d

A In su la tio n

3" P ip e in su la tio n w ra p

St ai r l an di ng

B Ye llo w

/F ib ro us

N on e D et ec te d

A

W ra p 4"

P ip e in su la tio n w ra p St ai r l an di ng B

Ta n/

W hi te /S ilv er

/F ib ro us

N on e D et ec te d

A

In su la tio n 4"

P ip e in su la tio n w ra p St ai r l an di ng B

Ye llo w /F ib ro us N on e

D et ec te d

A W ra p

6" P ip e in su la tio n w ra p

St ai r l an di ng

B Ta n/ W hi te

/S ilv er /F ib ro us N on e

D et ec te d

A In su la tio n

6" P ip e in su la tio n w ra p

St ai r l an di ng

B Ye llo w

/F ib ro us

N on e D et ec te d

B

W ra p 6"

P ip e in su la tio n w ra p R m

D

Br ow n/ Si lv er

/N on

-F ib ro us

N on e D et ec te d

B

In su la tio n 6"

P ip e in su la tio n w ra p R m

D

Ye llo w /N on -F ib ro us N on e

D et ec te d

A W ra p

Pi pe fi tti ng o n 6" p ip e St ai r l an di ng B

W hi te /N on -F ib ro us N on e

D et ec te d

A In su la tio n

Pi pe fi tti ng o n 6" p ip e St ai r l an di ng B

Ye llo w /F ib ro us N on e

D et ec te d

Pa ge b e s t o s

S a m p l e

S u m m a r y

T a b l e

X G F G

B u i l d i n g

N o

Sa m pl e

La ye r M at er ia l

Lo ca tio n

La b

D es cr ip tio n

As be st os

C on te nt

I

W ra p

AC

d uc t i ns ul at io n

R m

D Br ow n/

Si lv er /F ib ro us N on e

D et ec te d

I In su la tio n

AC

d uc t i ns ul at io n R m

D

Ye llo w /F ib ro us N on e

D et ec te d

A W ra p

Pi pe fi tti ng o n 4" p ip e St ai r l an di ng B

W hi te /N on -F ib ro us N on e

D et ec te d

A In su la tio n

Pi pe fi tti ng o n 4" p ip e St ai r l an di ng B

Ye llo w /F ib ro us N on e

D et ec te d

A Fo am Fo am p ip e in su la tio n on

" P

VC

p ip e ch as e R m

D

Ye llo w /N on -F ib ro us N on e

D et ec te d

I D uc t T ap e

Si lv er D uc t T ap e

R m

D Ta n/ Si lv er

N on e D et ec te d

I

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" V in yl fl oo r t ile w ith b la ck s pe ck s R m

A

G ra y/ N on -F ib ro us N on e

D et ec te d

I M as tic

" V in yl fl oo r t ile w ith b la ck s pe ck s R m

A

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D et ec te d

A C ov e

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R m

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N on

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N on e D et ec te d

A

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A

Ta n/

N on

-F ib ro us

N on e D et ec te d

A

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Ti le

2' X2

' W hi te c ei lin g til e R m

A

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D et ec te d

A C om po si te

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W hi te /B lu e/

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N on e D et ec te d

A

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R m

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" V in yl fl oo r t ile w ith b ro w n st re ak s

R m

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D et ec te d

A Vi ny l

Vi ny l c ov er ed w al l b oa rd R m

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Fi br ou s

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A

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H an ge r

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/N on

-F ib ro us

N on e D et ec te d

A

In su la tio n W al l i ns ul la tio n w ra p

H an ge r

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A

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R m

A G ra y/

N on

-F ib ro us

N on e D et ec te d

A

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2B W hi te

/N on

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A

M as tic

" V in yl fl oo r t ile O ut si de R m

2B Br ow n/

N on

-F ib ro us

N on e D et ec te d

A

W ra p W hi te p ip e in su la tio n to h ea te r St ai r C st

L ev el Ta n/ W hi te

/S ilv er N on e

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A In su la to n

W hi te p ip e in su la tio n to h ea te r

St ai r C st L ev el

Ye llo w /F ib ro us N on e

D et ec te d

A C on cr et e

C on cr et e sl ab H an ga r G ra y/

W hi te /N on -F ib ro us N on e

D et ec te d

A C au lk

C au lk a ro un d ex te rio r d oo r f ra m e

Ex te rio r

G ra y/ N on -F ib ro us N on e

D et ec te d

A Be ig e

La ye r Ex te rio r s tu cc o

Ex te rio r

Be ig e/ N on -F ib ro us N on e

D et ec te d

A G ra y

La ye r Ex te rio r s tu cc o

Ex te rio r

G ra y/ Fi br ou s N on e

D et ec te d

A In su la tio n

Ex te rio r s tu cc o Ex te rio r W hi te

/N on

-F ib ro us

N on e D et ec te d

A

C au lk C au lk a ro un d ex ha us t v en t

Ex te rio r

W hi te /N on -F ib ro us N on e

D et ec te d

A Sk im C oa t

Sk im

C oa t o ve r m et al Ex te rio r G ra y/

Ta n/

N on

-F ib ro us

N on e D et ec te d

A

C au lk C au lk a ro un d ro ll up d oo rs

Ex te rio r

Ta n/

N on

-F ib ro us

N on e D et ec te d

Pa ge

Attachment E

WDNR Form 4500-113, WDNR Asbestos Publications, and Information on Identifying, Handling, and

Properly Disposing of Hazardous Materials

(WDNR Guidance WA-651)

Wisconsin Department of Natural Resources Waste & Materials Management Program 1

Before beginning any demolition or renovation project, it is important to know about harmful materials that may be present on your project site.

This guide walks contractors and building owners through the steps to identify harmful materials commonly found at project sites and to handle and dispose of them safely. It also offers proper ways to manage recyclable and reusable materials and other wastes that are common in demolition and renovation projects.

The Resources section on the last page has links to websites with more information.

Note: This document is not intended as a substitute for reading the rules, regulations, and statues related to handling demolition and renovation debris. It is simply a guide to assist you in determining how they apply to your demolition or renovation project.

COMMON HARMFUL MATERIALS

Buildings can contain a number of harmful materials that may expose workers and the public to serious health risks and pollute the air, land and water if handled or disposed of in an unsafe way. Five of these harmful materials are common on project sites and need special care in

Asbestos

PLANNING YOUR DEMOLITION

OR RENOVATION PROJECT:

(Formerly called Pre-Demolition Environmental Checklist)

PLANNING YOUR PROJECT

INFORMATION ON IDENTIFYING, HANDLING AND PROPERLY DISPOSING OF HAZARDOUS MATERIALS

WA-651 (Revised 2013) c Conduct a walk-through of the project building(s) and grounds to and other site-related concerns.

c with specialized inspectors or contractors, if necessary c demolition or renovation activities prior to starting any demolition or renovation work.

c to remove and properly manage harmful materials prior to starting your project.

c for the disposal of harmful and non-harmful materials related to the project to avoid potential enforcement action.

2 Guide to Hazard Evaluation, Recycling and Waste Disposal

STEP 1. Conduct a walk-through of the project building(s) and grounds to identify items that contain harmful materials and other site-related concerns.

Identifying hazardous materials before starting work on a project site protects worker health and safety, building

Doing this up front can help you choose the appropriate inspectors, consultants and contractors and avoid costly change orders or project delays.

Before you begin any demolition or renovation project, thoroughly inspect and inventory the project site for the

• Appliances may contain CFCs, mercury or PCBs. Appliances that contain CFCs or PCBs must be processed by an appliance de-manufacturer registered with the DNR.

All layers of materials, behind walls, ceiling spaces, etc., should be inspected and sampled unless they are assumed to contain asbestos. The following building components may contain asbestos, but this list is by no means all-o Used around windows, doors, two materials are joined. PCBs have also been found in caulking materials. Schools and industrial buildings constructed or renovated between 1950 and 1979 are suspected to contain PCB-containing caulk.

o Including acoustical tiles and adhesives, and the materials listed under “Interior and exterior walls” below. All ceiling layers and any spaces above the ceiling where drop ceilings are present should be checked.

Insulation debris may also be lying on top of ceiling tiles.

o Insulators; spark arrestors and transite panels in electrical boxes; wiring insulation; ducts/conduits (transite pipe); and light o o Duct, pipe, and joint insulation because elbows/joints are often coated with connectors; packing/gaskets and adhesives;

carpet, etc.); and grout and felt paper under o Blown-in, spray-applied, and block.

o Wall plaster; joint compound; patches; transite wallboard and mortar; asphalt shingles/siding; felt under siding, stucco, textured paint, and other spray-applied materials. Paint containing asbestos is rare except in commercial applications, where it was usually applied as a very thick, often silver-colored coating or added to textured paints.

o Appliances with a heating and blankets; laboratory tabletops; fume hood like gloves, hoods, aprons, etc.

o Pipe wrap, pipe joints, transite counter tops in bathrooms, faucets, packing gaskets, and adhesives.

o Asphalt shingles; tar-type coatings which are often around vents, chimneys, etc.;

mag-block type material found under other

Switches for lighting may use mercury relays. Look for any control associated with exterior or automated lighting systems, such as “silent” wall switches.

Several types of light bulbs or lamps contain mercury and must be properly legitimately recycled o Even the newer lamps with green-colored ends contain mercury.

o metal halide, high pressure sodium, mercury vapor.

o

• Mercury may be found in thermometers, barometers, thermostats, blood-light bulbs. Any equipment used for measurement

FIVE STEPS TO A SUCCESSFUL DEMOLITION OR RENOVATION PROJECT

Wisconsin Department of Natural Resources Waste & Materials Management Program 3 most commonly associated with commercial and industrial equipment systems, including tanks, boilers, furnaces, heaters, electrical systems, water cleaning systems, and systems for the movement or pumping of gas (air) or liquids (water). In addition, mercury containing devices are also common in certain agricultural operations such as dairy, and may be present in older model consumer appliances and residential properties, especially larger multi-unit properties.

• Used oil in containers or tanks, hydraulic oils in machinery, electrical transformers and capacitors, and elevator shafts. These oils may contain PCBs and may need to be tested to determine if the oil can be recycled or must be properly disposed of.

• Residential and industrial paints may contain lead, solvents or asbestos. Some industrial paints may contain PCBs.

In addition to the items listed above, be aware of these

• Unused and improperly abandoned wells can directly channel contaminated surface water into the groundwater.

State law requires that all wells and drill holes construction work on the property.

• Batteries may be found in smoke detectors, emergency lighting systems, elevator control panels, exit signs, security systems and alarms. Batteries should be separated from other wastes and taken to a recycling facility or a business that accepts batteries for recycling.

• Most and must be recycled. These can contain hazardous materials such as lead, cadmium, chromium, and mercury and, if not recycled, may be regulated as hazardous waste.

• Many self-luminous exit signs contain tritium, a radioactive material. All self-luminous exit signs must have a permanent material. The label will also include the name of the manufacturer, the product model number, the serial number, and the quantity of tritium contained. It is illegal to abandon or dispose of these signs except by sending them to the manufacturer or to others licensed by the U.S.

Nuclear Regulatory Commission.

HAZARDOUS AND

UNIVERSAL WASTES

Some wastes, such as used or unused solvents, sanitizers, paint wastes, chemical wastes, pharmaceuticals, gas cylinders, aerosol cans and pesticides, may be hazardous waste and regulated by the EPA and DNR. Hazardous wastes must be removed from a project site prior to demolition or renovation and be disposed publication “Is Your Waste Hazardous?” (WA- 1152) at wa1152.pdf to determine if a waste is hazardous.

See Handling and Disposal Choices on page 7 for information on how to dispose of hazardous wastes on a project site.

Universal wastes are hazardous wastes that can be collected and transported with fewer regulations. Universal wastes include hazardous waste batteries, certain pesticides, mercury thermostats and other mercury-containing equipment and some lamps (light bulbs). In Wisconsin, antifreeze can also be managed as a universal waste if it is recycled. See chapter NR 673 of Wisconsin Administrative Code for more details on recycling and reusing universal waste.

• Walls and foundations often contain painted concrete. With prior DNR approval, contractors can grind the concrete and use it on-site or nearby under a new building or road.

• The smoke detectors that contain a small amount of radioactive material will be labeled and should be returned to the manufacturer for disposal. Otherwise, smoke detectors may go in the trash.

consultant can conduct environmental property contaminated soil.

• In Wisconsin, all spills of hazardous substances that negatively affect or threaten to negatively affect public health, welfare or the

4 Guide to Hazard Evaluation, Recycling and Waste Disposal

OPEN BURNING

It is illegal to burn painted, treated or unclean wood, asphalt, plastics of any kind, oily substances, tires and other rubber products, garbage, recyclables, wet rubbish, and other materials. Demolition materials that cannot be electrical wiring, cabinetry and countertops, and plastic plumbing.

Burning of clean, unpainted and untreated wood is allowed with a DNR burning permit using DNR-approved methods. When burning this type of wood from demolition waste, you must separate out all of the illegal materials, including painted or treated wood, before any burning occurs. The DNR encourages chipping clean, untreated wood for mulch or ground cover.

If you do decide to burn clean, unpainted and untreated wood, it is your responsibility to know what restrictions apply in the area where you are burning. Remember, you must also follow local burning ordinances that may be more information on local burning rules.

asbestos program coordinator at (608) 266-3658.

REUSE AND RECYCLING OF MATERIALS

inventory the project site for harmful materials, take note of materials that can be reused or recycled and remove them from the project site before demolition work begins.

•The Wisconsin Business Materials Exchange is a web service that facilitates the reuse of surplus or unwanted items or materials among businesses, institutions, and organizations. You can use this tool to post items that are available and request an item you may need.

harmful materials have been removed.

•Clean brick, building stone, concrete and asphalt can be stockpiled for crushing and reusing in future building projects.

•Clean, untreated wood can be recycled or chipped for mulch or ground cover.

•Many items such as appliances, electronics, paper and cardboard, glass containers and vehicle items are dnr.wi.gov and search “what to recycle.”

•The online Wisconsin Recycling Markets Directory contains a list of self-identifying businesses accepting recyclable materials. Make sure your chosen recycler meets local, state and federal regulatory requirements.

•Demolition debris may be taken to a construction and demolition recycling facility if all harmful materials, including all types of asbestos, are removed prior to demolition or renovation.

Wisconsin Department of Natural Resources Waste & Materials Management Program 5 environment must be immediately reported to the DNR via the Spills Hotline, 800-934-0003.

• Chemical tanks (underground and aboveground) and septic tanks should be assessed, emptied and decommissioned.

• Tires should be reused or recycled. Your can check WisconsinRecyclingDirectory.com and search for “motor vehicle items” and then “tires.”

STEP 2. Identify and quantify harmful materials at your job site with specialized inspectors or contractors, if necessary

Department of Natural Resources and the Department a project site. See the sections on asbestos and lead in this step for those requirements.

You can identify other harmful materials on a project site, such as CFCs and halons, mercury, and PCBs, by doing an inventory of the building systems and materials. The DNR recommends hiring an inspector these materials and can collect samples, if necessary, If you have a large or complex project, it may make sense to hire a consultant to oversee the coordination

Asbestos Health risks: Asbestos is a known human carcinogen that can cause serious health problems when disturbed and inhaled. Historically, asbestos was commonly used in industrial, commercial, and residential structures.

Asbestos is still used today but to a lesser extent.

Location and/or materials: Asbestos is used in more than 3,000 building materials. Asbestos is commonly found in HVAC systems, electrical systems, blankets, laboratory tabletops, fume hood lining, for a detailed list of building materials and locations that may contain asbestos.

The Department of Health Services requires licensed inspectors to identify asbestos. Inspectors can assume asbestos to be present, or they can identify it through testing. The DNR requires an asbestos inspection for certain projects and recommends it for others.

• Two or more contiguous single family homes

• Homes that are part of a larger demolition project

• Industrial, manufacturing or commercial buildings including bridges, farm buildings, and churches exercise

• Single family homes

• Multi-family housing with 2–4 units

Inspection must be completed and asbestos materials must be removed before beginning any demolition or renovation activities.

Health risks protective ozone layer high in the atmosphere, allowing rays. Some of the harmful effects of increased UV exposure include increased risk of skin cancer, eye damage.

Location and/or materials in refrigerants in rooftop, room and central air conditioners, refrigerators, freezers, and chillers, coolers, walk-in coolers (refrigeration or cold storage areas), vending machines and food display cases.

control equipment.

Health risks: Inhaling or swallowing lead dust can cause serious health effects, including kidney disease, neuropathy, infertility, heart and cardiovascular disease, 6 Guide to Hazard Evaluation, Recycling and Waste Disposal

Location and/or materials: Lead plumbing and lead-based paint are commonly found in many older buildings. Lead may be found in paint on woodwork and metal equipment, leaded glass, lead window-sash and solder. Lead is found in both indoor and outdoor applications. Lead is also found in lead-acid batteries associated with older lighting, exit signs, and security systems.

The Department of Health Services requires licensed inspectors and risk assessors to identify lead paint. When building surfaces or components are being renovated in any residential and child-occupied buildings built before 1978 (such as private homes, rental units, day care centers, and schools), lead paint must be assumed to be present or

Lead paint sampling is recommended on commercial and industrial projects. The US discontinued manufacturing lead paint for residential use by 1978, but lead is still used in specialty paints in commercial and industrial applications. Most buildings have multiple layers of paint, and all layers should be considered.

Health risks: Liquid mercury evaporates slowly at room temperature and gives off harmful vapors that are invisible and odorless. Breathing these vapors causes the most harm to people, but mercury can also be harmful when it comes in contact with broken skin or when it is swallowed. Women and children are most at risk from mercury poisoning, which can cause brain and nerve damage, resulting in impaired coordination, blurred vision, tremors, irritability and memory loss.

Mercury poisoning also causes birth defects.

Location and/or materials: Mercury may be found in thermometers, barometers, thermostats, dental other types of light bulbs. Any equipment used for are most commonly associated with commercial and industrial equipment systems, including tanks, boilers, furnaces, heaters, electrical systems, water cleaning systems, and systems for the movement or pumping of gas (air) or liquid (water). In addition, mercury containing devices are common in certain agricultural operations such as dairy, and may be present in older model consumer appliances, vehicle light switches and residential properties, especially larger multi-unit amalgam that may be found in sink drain traps. Mercury can also be found as part of older wastewater treatment

Health risks: PCBs may cause cancer in humans and can disrupt hormone and nervous system function. PCBs are persistent in the environment and consumption advisories for humans.

Location and/or materials: PCBs can be found in electrical oils (e.g. transformers and capacitors in appliances) electronic equipment, heat transfer paints, specialty paints (e.g. swimming pools) and caulking materials. Sumps, oil traps and concrete may be contaminated with PCBs as well. Electrical devices manufactured prior to 1978 should be assumed to contain PCBs.

You may be able to determine PCB concentrations in electrical equipment manufacturer indicating the PCB concentration at the time of manufacture, or service records showing the PCB concentration measured when the equipment was serviced. If a manufactured date and PCB content label are not found on a transformer or capacitor, the oil should be tested to determine the PCB content prior to labeled “No PCBs” may still contain PCBs, but at a concentration lower than what the EPA regulates. The oils in this equipment should still be tested to see if they contain PCBs and then handled appropriately.

Testing of specialty paint, epoxies and caulks in buildings built or renovated between 1950 and 1979 is recommended. High levels of PCBs are being found in these materials across the country. Once testing is complete, boldly label all surfaces and items that were found to contain PCBs so they are handled appropriately during renovation or demolition.

Wisconsin Department of Natural Resources Waste & Materials Management Program 7

3STEP 3. Notify the DNR of demolition or renovation activities prior to starting any demolition or renovation work.

• Two or more contiguous single-family homes

• Homes that are part of a larger demolition project

• Industrial, manufacturing or commercial buildings including bridges, farm buildings, and churches exercise projects meeting any of these criteria, if asbestos removal is involved.

All demolition projects meeting the previously listed before the project work begins.

All renovation projects meeting the previously listed

10 working days before the project begins.

Note: While plans to demolish or renovate a single-recommended you take the precautionary steps outlined in this publication.

HANDLING AND DISPOSAL CHOICES

You have a few options for handling and disposing of lead, mercury, PCBs and other wastes from your project site that qualify as hazardous waste. Identifying these options prior to beginning the project can help you schedule transportation and disposal and maintain the overall project schedule.

• to pick up and dispose of hazardous wastes. This takes the guess work out of handling these types of wastes. Contractors have properly trained personnel that will determine appropriate packaging, shipping and vehicle licensing and have established relationships with disposal facilities.

Other choices provide you with reduced regulation and may change depending on the amount of hazardous waste generated in a month. As a contractor, you may manage hazardous wastes you generate at temporary job sites only according to the following options. For more details on these options, see the DNR publication “Pilot Project for Management of Contractor Generated Hazardous Waste” (WA-654) at pdf/pubs/wa/wa654.pdf.

to transport the hazardous waste to a licensed or permitted hazardous waste treatment, storage and disposal facility. In this case, you must follow the applicable generator requirements in chapters NR 660-679 of Wisconsin Administrative Code.

In this case, the site owner must follow the applicable generator requirements in chapters NR 660-679 of Wisconsin Administrative Code. If you choose this option, be sure to include this in your contract with the site owner.

directly from the temporary job site to a Household and Very Small Quantity Generator (VSQG) Hazardous Waste Collection Facility. This includes county or municipal Clean Sweep locations. If the total quantity of hazardous waste generated by your company in one month is less than 220 lbs. (about half of a 55-gallon drum), you would be a VSQG and your hazardous waste may be taken to a Clean Sweep location for handling and disposal. Contact your local Clean Sweep coordinator for information on possible fees, accepted materials, and other details.

This option is currently available under a pilot project.