New York State Policies on Vermiculite and Vermiculite Containing Materials

By Ed Cahill
Vice President, Asbestos Division, EMSL Analytical Inc.

On June 22, 2012 the New York State Department of Health (NY DOH) issued a guidance letter outlining its policy on asbestos testing of materials containing vermiculite. This was a clarification and guidance with respect to an earlier FAQ the department released on April 8, 2011. To summarize, any loose fill vermiculite such as Vermiculite Attic Insulation (VAI), block fill, packing material etc. must be treated as Asbestos Containing Material (ACM). No analysis is necessary and in fact no laboratory analysis results will be deemed adequate to classify this material as non ACM.

The real surprise however was that in addition to loose fill vermiculite, any building material with >10% vermiculite as a component must also be treated as ACM! Fortunately this applies to relatively few types of building materials. Unfortunately one of the sample types it does apply to is spray-on fireproofing. The implications here are great for many large building owners.

Spray on fireproofing is, as the name implies a fire proof insulation that is literally sprayed onto the structural steel of buildings to protect it in case of fire. In an intense fire this insulation can make the difference in whether a building remains standing or collapses. Asbestos was an obvious component to add to spray on insulation since it is fireproof and an excellent thermal insulator. Due to the now well understood hazards of asbestos inhalation the EPA banned the use of sprayed on insulation containing asbestos in 1973. New formulations were created after that with no asbestos deliberately added. Ironically asbestos was still often present due to asbestos contamination in the vermiculite used. The most common source of vermiculite for over 70 years was the now closed vermiculite mine in Libby Montana. Vermiculite from this mine can contain a considerable amount of asbestos, both regulated and non-regulated. Since vermiculite is only one component in common spray on insulations such as W.R. Grace’s Monokote 5 or Isolatek’s Cafco 300, the final percentage of asbestos is often determined to be <1% by a typical asbestos analysis by PLM. Other components can include gypsum, calcium carbonate, cellulose, cement and mineral wool.

With the policies outlined in the June 2012 guidance document many New York building owners are facing a new reality, including major financial implications. Spray on fireproofing that was determined to be non-detect or <1 percent asbestos (non ACM) from surveys and lab analyses performed prior to the revised NYS guidance, now would be classified as ACM (asbestos containing material) because the vermiculite content is estimated to be >10 percent!

Beyond the June 22, 2012 letter little additional guidance was provided and asbestos consultants and laboratories struggled to interpret the guidance and strive for compliance. In response to growing concerns from all corners of the industry the Department of Health issued another three page guidance letter dated July 9, 2013 which allowed for an interim testing alternative to be used on materials with >10% vermiculite. This alternative testing method is the existing NY ELAP (Environmental Laboratory Approval Program) method 198.6 Polarized Light Microscopy (PLM) method that is used for non-friable organically bound samples such as floor tiles and mastics. With this method a material with >10% vermiculite may be classified as non-ACM, but with a catch. If this alternative method is used, the following “conspicuous disclaimer” must be added to the sample report.

“This method does not remove vermiculite and may underestimate the level of asbestos present in a sample containing greater than 10% vermiculite.”

Ironically this disclaimer must be placed on the report even if the material is determined to be >1% asbestos and classified as ACM!

The guidance letter explains that this alternative method is to be used “until new testing methods are established that effectively remove vermiculite from test samples and accurately identify asbestos.”
No information is provided as to when that might happen or what that final method might look like. There are existing procedures, such as the one outlined in Analysis of Amphibole Asbestos in Chrysotile and Other Minerals by Addison and Davies (1990). These involve hazardous chemical digestions with sequential boiling in acid and then a base. These are procedures best performed in a chemistry laboratory not your typical small scale asbestos analysis laboratory.

The unfortunate consequence is a current state of uncertainty and limbo in the industry on this issue. The requirement of placing the strong disclaimer on all reports when using the alternative testing method negates the ability to technically classify the materials as non-ACM for many end users of these data. In the face of this uncertainty building owners and their consultants are taking many various approaches:

Approach 1

  • Cancel or delay asbestos surveys if possible until final regulations are in place. This is likely affecting and delaying many real estate transactions.

Approach 2

  • If initial analysis determines vermiculite content >10% they are stopping. The material is treated as ACM.

Approach 3

  • If initial analysis determines vermiculite content >10% they are proceeding on to the alternative (additional) test method (ELAP 198.6) to determine the ASBESTOS percentage. Materials are classified as ACM or non-ACM accordingly and the disclaimer is tolerated or ignored.

Approach 4

  • Approach 2 or 3 are followed for regulatory compliance and then various additional preparation and analysis steps are requested. Transmission Electron Microscopy (TEM) analysis is very often part of this process as an effort to demonstrate the use of “Best Available Technology”.

As stated previously all loose fill vermiculite including Vermiculite Attic Insulation (VAI) and block fill insulation must be treated as ACM. There are no New York approved methods for the analysis of vermiculite and none may be used to try and classify this material as non-ACM. This ELAP position is aligned with the current EPA stance that there are currently no validated and approved analytical methodologies to accurately analyze and quantitate asbestos concentrations in vermiculite. The ASTM D22 Committee is currently working on a draft method for the qualitative analysis of asbestos in loose fill vermiculite by TEM. This method will likely go to ballot by years end and could possibly be finalized in 2014.

The steps necessary for compliance with the New York State policies regarding vermiculite containing materials are outlined in the latest guidance letter as a flowchart seen below.

For all friable (can be crushed by hand pressure) building materials the process begins with NY ELAP Method 198.1 Polarized-Light Microscope Methods for Identifying and Quantitating Asbestos Bulk Samples. This method is similar in many ways to the more widely used EPA 600 PLM method used in other states. With the new policies the first step is to examine the sample for its vermiculite component.

Scenario 1 Vermiculite <10%

  • If the vermiculite is determined to be ≤10% then the sample is treated like any other friable sample and analysis by method 198.1 continues in order to determine asbestos percent.
  • NOTE 1: Method 198.1 and the guidance letter mandate that quantitation be performed by a point counting procedure. The point count technique can be a more accurate quantitation technique than the more common calibrated visual estimation (CVE) technique used in most circumstances in other states. But it requires a microscope slide preparation that is as close to a monolayer as possible. Due to its relatively large size vermiculite in most cases is not conducive to a good (and accurate) point count.
  • NOTE 2: This critical part of the analysis is being applied unevenly from lab to lab with some labs attempting to differentiate between vermiculite and other micas that might be in the sample. The result can be large discrepancies in vermiculite estimates from lab to lab.
  • Vermiculite Attic insulation (VAI) by PLM

Scenario 2 Vermiculite >10%

  • If point counting by method 198.1 determines the vermiculite content to be greater than 10% this analysis is terminated (no asbestos determination is performed).
  • The analyst proceeds with analysis via ELAP method 198.6 Polarized-Light Microscope Method for Identifying and Quantitating Asbestos in Non-Friable Organically Bound Bulk Samples
  • This method requires special preparation steps to remove and track the weight loss of organic and acid soluble matrix material prior to analysis. It will not remove vermiculite unfortunately.
  • Asbestos analysis by PLM is performed on the resulting residue. The weight loss is included in the calculation of the final asbestos percent.
  • NOTE: Differentiation between the regulated and non-regulated asbestos types that are found in the common Libby vermiculite can be difficult by PLM. TEM is superior for this.
  • Regardless of whether or not the material is determined to be ACM (>1%) or non ACM (<1%) the following disclaimer must be added:

“This method does not remove vermiculite and may underestimate the level of asbestos present in a sample containing greater than 10% vermiculite.”

The current uncertainty in regards to vermiculite containing materials is unfortunate and has many agencies, regulators, building owners and consultants sitting on the sidelines waiting for more clarity. Those that are proceeding are faced with inconsistent application of existing guidance and the potential that their samples may need to be re-analyzed once the “final” method is adopted.

US Asbestos Epidemic

The Tennesseanby Jim Morris

International – Although asbestos use in the US plummeted from a peak of 885,000 tons in 1973 to 1,609 tons in 2008, the nation’s epidemic is far from over. As many as 10,000 Americans still die of asbestos-related diseases each year; one expert estimates that 300,000 or so will die within the next three decades.

“Ban Asbestos in America Act” Finally Passed in the Senate

After a long battle, the “Ban Asbestos in America Act” was finally passed in the Senate in October, much to the relief of advocates for asbestos victims and many others fighting to cease use of the known carcinogen. Celebrations for the ban will have to wait, however, since the final draft of the bill fails to block all asbestos-containing products. As a result, many who initially favored the bill are now disputing its approval.  In early October, every Senate member voted for the Act, first introduced by Senator Patty Murray (D-Wash.). Scientists and physicians supported it as well, along with victims and widows who have suffered from the effects of the dangerous substance. Proponents of the bill were disappointed to learn that the language had been watered down and much of what they had fought for had been omitted.

New Method of Tearing Down Asbestos Contaminated Home “Probably Safe”

A test in December 2007 of a new method for tearing down asbestos-contaminated buildings is probably safe, but concerns still exist, according to experts assembled by the federal government.  The Oak Hollow Apartments are secured as Fort Worth and the EPA prepare to demolish them this week. An experimental method will be used to dispose of the buildings with asbestos, with hopes that the method is safer and more cost-effective.  The Environmental Protection Agency, with cooperation from the city of Fort Worth, will demolish a portion of the vacant Oak Hollow Apartments using an updated version of what’s called the “wet method,” or “Fort Worth method.” The method, which is still in the experimental stages, has drawn the opposition of some environmentalists, who said Monday that they could not garner enough support to stop the testing.  A successful test could help pave the way for federal approval of the first new asbestos abatement method in decades and potentially make it cheaper to demolish buildings that have become eyesores and neighborhood dangers nationwide.

Murray to Push for Nationwide Ban

Sen. Patty Mrray (D-Wash.) will launch her push this week for a nationwide ban against asbestos when she chairs a hearing and introduces new legislation on the topic.

The substance has not been completely banned in the United States. The United States currently imports over $100 million worth of asbestos products annually, including brake pads and linings, cement pipe and floor tiles, according to Murray’s staff.

An EPA attempt to ban asbestos under the Toxic Substances Act failed in October 1991, when the 5th U.S. Circuit Court of Appeals revoked the ban because EPA hand not chosen the “least burdensome regulation” to protect public health and environment as required by the act.

The hearing is set for 10:00 a.m., Thursday March 1 in 430 Dirksen.

EPA Fines 7 Tucson Charter School Operators $67, 240 for Asbestos Violations

(08/06/07) SAN FRANCISCO — The U.S. Environmental Protection Agency recently fined seven Tucson charter school operators a combined total of $67,240 for Asbestos Hazard Emergency Response Act violations.

In May 2006, EPA inspectors discovered the school operators all failed to conduct inspections to determine if asbestos-containing material was present in school buildings and failed to develop asbestos management plans.

Abuse of Epidemiology

Much of the “debate” about the relationship between asbestos exposure from automobile brake work and asbestos-induced cancer has been fueled by studies that have been funded by corporations with billions at stake in tort litigation. Evidence exists that asbestos-lined brake manufacturers have corrupted medical literature to escape liability, analyzing studies funded by these companies to enable them to claim that work with asbestos brake linings never causes mesothelioma.

OSHA Q&A

Inspection Procedures for Occupational Exposure to Asbestos Final Rule 29 CFR Parts 1910.1001, 1926.1101 and 1915.1001.

How to Improve Your Indoor Air Quality

ASHRAE defines acceptable indoor air quality as air in which there are no known contaminants at harmful concentrations as determined by cognizant authorities and with which 80% or more people exposed do not express dissatisfaction. Indoor air quality in commercial office buildings is important because it can affect occupant comfort, health, and work productivity. Scientific studies have confirmed a direct correlation between poor indoor air quality and increased employee sick days and workers compensation claims. Therefore, improving indoor air quality in commercial office buildings is a benefit to both business employees and owners.

There are a variety of factors that can contribute to poor indoor air quality in the workplace. This article addresses certain parameters of indoor air such as temperature, relative humidity, carbon dioxide concentrations, carbon monoxide concentrations, volatile organic compound (VOC) concentrations and small particle concentrations; however, it is important to note that there are other factors that can negatively affect indoor air quality.

Thermal conditions (temperature and relative humidity) should be maintained within recommended ranges found in ASHRAE 55.2004 to maximize occupant comfort levels. Additionally, controlling relative humidity within the space can also prevent mold growth from occurring. The presence of mold growth within an indoor environment can cause occupants to experience allergy type symptoms. Elevated indoor carbon dioxide concentrations from under-ventilated office areas can cause occupants to feel fatigued. Elevated indoor carbon monoxide concentrations from combustion equipment or nearby parking garages can present a hazardous condition for building occupants being that carbon monoxide is a highly toxic gas which is lethal when exposed to elevated concentrations.

Volatile organic compounds (VOCs) from office furniture, flooring, paints, printers, copiers, cleaning products and deodorizers can cause adverse reactions in certain occupants. Typical symptoms of elevated indoor VOC concentrations have been described as coughing, sneezing, allergy type symptoms, and burning or itching eyes.

Excessive small indoor particle concentrations (particles that are small enough to enter the respiratory system) can be a result of insufficient cleaning activities, excessive paper shredding or construction activities and can cause building occupants to experience symptoms similar to those experienced by elevated VOC concentrations.

So what can be done to improve indoor air quality? Best practice would be to implement monitoring equipment that continually measures the indoor air quality parameters mentioned above. Continuous measurement of the indoor air would enable a building manager to not only confirm that the indoor air quality is within industry acceptable levels, but also detect any changes in the indoor air quality so that corrective measures could be performed prior to receiving occupant complaints.

Another good practice is to install high efficiency filtration (within the static capability of the HVAC systems) throughout the building. A filter maintenance schedule should also be developed to prevent the use of dirty filters. Routine cleaning procedures should be performed throughout the building. Appropriate ventilation rates should be ensured to effectively dilute indoor contaminants and to reduce carbon dioxide concentrations within the building. The selection of certain building materials and components such as low-emitting VOC paints, flooring, furniture, and low-emitting copiers and printers will limit the amount of contaminants introduced into the indoor environment.

Maintaining good indoor air quality is an ongoing effort that requires an understanding of factors that can negatively impact indoor air and the appropriate preventative measures that should be implemented.