Erionite was identified in SW North Dakota (Killdeer Mountains) by Nels Forsman (1986) Erionite is a naturally occurring acicular or “fibrous” zeolite.

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Presentation transcript:

Erionite was identified in SW North Dakota (Killdeer Mountains) by Nels Forsman (1986) Erionite is a naturally occurring acicular or “fibrous” zeolite mineral that may pose a cancer risk from inhalation In 2006 the EPA Dunn Co. ND investigations prompted evaluations in equivalent geologic units in the Tri-state area of NW South Dakota and SE Montana Literature documented erionite in other western states AZ, CA, CO, ID, NM, NV, OR, UT, WY (R.A. Sheppard USGS 1996)

Hexagonal cage-like structure of linked (Si, Al)O 4 tetrahedra Chain-like structure with 6 tetrahedra on each edge of a unit Very hygroscopic, absorbs up to 20% its weight in water Ca 3 K 2 Na 2 [Al 10 Si 26 O 72 ].30H 2 O

Source: MDoT & EPA µm frame width 1-3 % erionite by PCM

Erionite is detected within Tertiary “butte capping” formations mapped as the Arikaree and White River Formations including the Brule, and Chadron members within the Western Dakotas- SE Montana Region Occurrence is primarily associated with dissolution of Oligocene-Miocene silicic ash fall tuffs followed by in situ re-crystallization

MT ND SD

Arikaree Brule Chadron

Arikaree-White R. Bedrock Units CNF Land Units Carter Co. MT Harding Co., SD Bowman Co., ND

Arikaree Brule

Chadron Brule

Erionite concentrations vary within individual geologic units (Arikaree and White River including Brule and Chadron) Bedrock samples ranged from trace ( %) to 20% erionite by volume The Arikaree and Brule Formations appear to generally contains between 5% to 15% erionite Chadron Fm. appears to contain less erionite, may be related to bentonitic alteration Gravel Pits developed in Fort Union Formation contain non-detection to <1%

Fiber size and shape that allows respiration (<1 micron), retention in lungs, and translocation to the pleural lining Durable, persistent in tissues Reactive surfaces (erionite is extremely adsorbent and hygroscopic) High collective surface area (erionite = 200 m 2 /gram versus amphibole asbestos =15 m 2 /g) Propensity to split into thin fibers in vivo (unknown)

Source: USGS Lowers & Meeker 2007

N=94 Yes - approx 30% of mineral bundles were <1 micron, but what size are the fibrils? Source: Dunn Co., ND USGS Lowers & Meeker 2007

Previous animal studies used Oregon and Turkish erionite for both intrapleural inoculation and inhalation, erionite produced very high cancer response rates –sometimes up to 100% Animal cancer response to erionite was much more rapid than with asbestos exposures and indicates substantially more immune response and possible carcinogenicity Was there genetic predisposition in Turkey or was duration and/or timing of the dose?

Source: Lowers & Meeker USGS 2007

Difficult to quantify level and duration of outdoor exposure (road dust, firewood harvesting, recreation) Time since and type of first exposure (childhood exposure may be significant) Despite apparent supertoxicity, long latency period for disease still observed in Turkish population Trace concentrations ( %) in samples still represent millions of fibers in the bulk sample and a potential inhalation exposure hazard when disturbed

EPA and North Dakota initiated a study to evaluate observable health effects in the Dunn Co. area Sought 100 volunteers for testing Received approximately 35 volunteers to be tested Findings of ND health study to be released in June-July, 2010

Testing for Erionite presence prior to land management actions Use of appropriate asbestos worker PPE such as Respirator, Tyvex, Gloves Prevent or reduce dust generation Wetting ground disturbance during work Use of binder such as Magnesium Chloride Use of erionite non-detect aggregate sources

Sample collection and analysis across the Sioux Ranger District, CNF Sampling strategy focused on - Occurrence (detect vs. non-detect) - % erionite composition by volume -Strategy also aimed at testing White River Group vs. Arikaree Fm. No attempt was undertaken to define if or where an erionite “enrichment zone” occurs

Large mountaintop removal of Arikaree Fm. on MT Hwy S-323 occurred in the mid-1960s Erionite containing material was used over 3+ miles of highway project primarily as fill Highway maintenance worker protection measures are the same as used in Libby Asbestos NPL site including: Air purifying respirators, Tyvek suits and nitrile gloves, equipment decontamination, and HEPA vacuum equipment interiors

EPA studies initiated in 2006 to assess erionite outdoor exposures in Dunn Co. Initiate health study to assess the health effects of erionite exposure in North Dakota ND DoT initiated special provisions on aggregate testing within estimated areas of erionite occurrence State has required increasingly stringent testing for erionite in other locations

Erionite is present within Tertiary units in the Tri-State area including large areas within the USFS Custer National Forest Erionite composition and “fiber” size are comparable to disease areas of Turkey and analogous to asbestiform mineral exposures No clear U.S. regulatory direction exists and further exemplifies the need for a national policy on natural occurrences of asbestos (NOA) & erionite

Erionite is not confined to the Tertiary ash-bearing units but also exist in the underlying Tertiary Fort Union and in eroded and transported sediments Take no land management actions which increases the exposure potential and protect workers performing maintenance and disturbance activities

Perform additional erionite toxicity testing based on fiber chemistry and fibril size with Tri-State area samples, Conduct exposure-based assessments in forest settings such as unpaved road travel, recreational, and fire fighting scenarios, Develop a national policy regulatory framework for NOA and erionite