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Ambient Concentrations of Mineral Fibers in Air and Water in Northeast Minnesota

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Ambient Concentrations of Mineral Fibers in Air and Water in Northeast Minnesota AMBIENT CONCENTRATIONS OF MINERAL FIBERS IN AIR AND WATER IN NORTHEAST MINNESOTA Minnesota Environmental Quality Board Author: Peter Ashbrook Date: September, 1978 Final Draft i INTRODUCTION TO THE REGIONAL COPPER-NICKEL STUDY The Regional Copper-Nickel Environmental Impact Study is a comprehensive examination of the potential cumulative environmental, social, and economic impacts of copper-nickel mineral development in northeastern Minnesotac This study is being conducted for the Minnesota Legislature and state Executive Branch agencies, under the direction of the Minnesota Environ­ mental Quality Board (MEQB) and with the funding, review, and concurrence of the Legislative Commission on Minnesota Resources. A region along the surface contact of the Duluth Complex in St. Louis and Lake counties in northeastern Minnesota contains a major domestic resource of copper-nickel sulfide mineralization. This region has been explored by several mineral resource development companies for more than twenty years, and recently two firms, AMAX and International Nickel Company, have considered commercial operations. These exploration and mine planning activities indicate the potential establishment of a new mining and pro­ cessing industry in Minnesota. In addition, these activities indicate the need for a comprehensive environmental, social, and economic analysis by the state in order to consider the cumulative regional implications of this new industry and to provide adequate information for future state policy review and development. In January, 1976, the MEQB organized and initiated the Regional Copper-Nickel Study. The major objectives of the Regional Copper-Nickel Study are: 1) to characterize the region in its pre-copper-nickel development state; 2) to identify and describe the probable technologies which may be used to exploit the mineral resource and to convert it into salable commodities; 3) to identify and assess the impacts of primary copper-nickel development and secondary regional growth; 4) to conceptualize alternative degrees of regional copper-nickel development; and 5) to assess the cumulative environmental, social, and economic impacts of such hypothetical develop­ ments. The Regional Study is a scientific information gathering and analysis effort and will not present subjective social judgements on whether, where, when, or how copper-nickel development should or should not proceed. In addition, the Study will not make dr propose state policy pertaining to copper-nickel development. The Minnesota Environmental Quality Board is a state agency responsible for the implementation of the Minnesota Environmental Policy Act and promotes cooperation between state agencies on environmental matters. The Regional Copper-Nickel Study is an ad hoc effort of the MEQB and future regulatory and site specific environmental impact studies will most likely be the responsibility of the Minnesota Department of Natural Resources and the Minnesota Pollution Control Agency. i i ABSTRACT Total fiber levels in streams ranged from 0.4 t07~9 million fibers/ liter with chrysotile and '0.2 to 5 million fibers/liter without chrysotile. Hedian levels were 3.3 and 1 .. 5 million fibers/liter, respectively. These levels appear to be similar to levels reported elsewhere in the literature for rivers. lakes, beer, wine and soft drinks. Fiber levels ~n streams receiving minewater discharge from Reserve or Erie were not different from streams that-did, not receive such discharges. A snow sample had fiber levels similar to those in streams and similar to a previous report. Nineshaft water from the Amax shaft near Babbitt contained four billion fibers/liter of which 700 million were amphibole fibers. These levels are at least three orders of magnitude below estimates of levels discharged by Reserve into Lake Superior .. - - . Approximately four-five perc~nt of the particles from a gravel road 6ust sample, consisting of gravel from a gravel pit five miles west of Reserve's Peter Hitchell mine, was co;nposed of fibers.. Hany of these fibers had a length-t0-~idth ratio greater than ten. Approximately one-third of these fibers.v:erc a~phiboles. A similar sample collected from an Erie haul road five ~iles north of HOlt Lakes had less than one-t~o percc~t fibers . ... iii TABLE OF CONTENTS Page ABSTRACT i INTRODUCTION TO THE REGIONAL COPPER-NICKEL STUDY ii TABLE OF CONTENTS iii LIST OF TABLES iv LIST OF FIGURES v INTRODUCTION 1 METHODS 3 RESULTS 5 DISSCUSSION 7 CONCLUSIONS 9 REFERENCES 11 TABLES 12-27 FIGURES 28-31 APPENDIX 1. 32-33 APPENDIX II 34-52 APPENDIX III 53-62 iv LIST OF TABLES TABLE 1. Ambient concentrations and mean aspect ratio for fibers found on membrane air samples in 1977. TABLE 2. Hibbing Weather Data TABLE 3. Cascade impactor data from Hoyt Lakes (October 14~ 1977) TABLE 4. Ambient concentration and mean aspect ratio for fibers found in water samples TABLE 5. Amphi'bole and cnrysotile fiber concentrations compared to mean blank levels for water samples TABLE 6. Air sampling program at Silver Bay~ Minnesota TABLE 7. Comparison of fiber levels* found in air TABLE 8. Comparison of fiber levels* in water samples v LIST OF FIGURES F\IGURE 1 G Location of air quality monitoring sites FIGURE 2. Location of water quality an~ road dust monitoring sites FIGURE 3. Wind direction on days of highest and lowest fiber levels Page 1 INTRODUCTION Mineral fibers present a potentially serious, but presently poorly under= stood, environmental health hazard for the non-occupational population in bmth Minnesota, as evidenced by the Reserve Mining controversy, and nation~ wide (Carter, 1977). This poor understanding can be attri~uted partly to confusion over and misuse of terminology, and incomplete knowledge of the mechanism by which fibers affect health. Asbestos is used as a collective mineralogical term encompassing the asbesti­ form varieties of various silicate minerals and is applied to a commercial product obtained by mining primarily asbestiform minerals (Campbell, et al. 1977). Five minerals fit this definition: chrysotile (a member of the serpentine group), and the asbestiform varieties of actinolite-tremolite; anthophyllite, cummingtonite-grunerite, and riebeckite (members of the am­ phibole group). Chrysotile always'occurs in the asbestiform habit, amphiboles usually occur in non-asbestiform habits, with the exception of riebeckite, which usually occurs in the asbestiform habit as crocidolite. Asbestiform minerals occur as fibers, which display some resemblances to' organic fibers in terms of circular cross section, flexibility, silky surface luster, and other characteristics. Cleavage fragments, such as those produced from crushing and processing non-asbestiform minerals~ do not satisfy this definition of fibers and should De considered "fiber-like. 1I When asbestiform and non-asbestiform minerals are subjected to crushing and processing, the resulting fragments have minor differences in morphology and physical properties that are very difficult to distinguish under a transmission electron microscope. For this reason, when the transmission electron.microscope is used, fibers are defin~d as fragments with aspect (length to width) ratio of 3:1 or greater, even though many of these Page 2 fragments may not meet the mineralogic definition of a fiber. In this paper the term IImineral fiber" will be used to denote both asbestos fibers arid cleavage fragments of non-asbestiform minerals because ambient levels of mineral fibers were determined by transmission electron microscopy, which did not distinguish between these two classifications. Mineral fibers have a number of possible sourceso Fragments can be generated from both asbestiform and non-asbestiform minerals by both human activities, such as mining and processing ore, construction, blasting, and drilling, and by natural processes such as mechanical effects from wind and water. Asbestos fibers may occur naturally; however, they are uncommon in northeast Minnesota. Mineral fibers may also be introduced to this region tnrough sources such as insulation materials, foods, and brake linings in motor vehicles. Asbestos fiber and non-asbestiform cleavage fragments have different characteristics in terms of tensile strength, flexibility, durability, and surface properties. The extent to which these differences are related to the harmful properties of asbestos is uncertain at this time. Occupational health standards of asbestos exposure are based upon fibers greater than five micrometers in width and a length-to-width (aspect) ratio of at least three. However, there is widespread belief that this definition of fibers is inadequate for health standards. Several theories"have been prop'osed as to how asbestos causes disease: the fiber theory, the trace metal theory, the organic material theory and the multifunctional theory (Regional Copper-Nickel Study 1977). Briefly, some believe that the physical characteristics of asbestos (such as aspect ratio or fiber diameter) are responsible for disease; others believe that trace metals associated with fibers cause disease; others believe that fibers serve as carriers for organic materials, which in turn cause disease; and still others believe that several or all three of these theories Page 3 may be operating concurrently. The Regional Copper-Nickel Study conducted a general survey of ambient fiber levels in water and air to characterize existing levels and to try to correlate these levels with suspected fiber sources near the Duluth Gabbro Contact. Ambient levels found in
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  • Modulated 2:1 Layer Silicates: Review, Systematics, and Predictions
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