Fluorescent Chrysotile from Sterling Hill, New Jersey
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NMAM 9000: Asbestos, Chrysotile By
ASBESTOS, CHRYSOTILE by XRD 9000 MW: ~283 CAS: 12001-29-5 RTECS: CI6478500 METHOD: 9000, Issue 3 EVALUATION: FULL Issue 1: 15 May 1989 Issue 3: 20 October 2015 EPA Standard (Bulk): 1% by weight PROPERTIES: Solid, fibrous mineral; conversion to forsterite at 580 °C; attacked by acids; loses water above 300 °C SYNONYMS: Chrysotile SAMPLING MEASUREMENT BULK TECHNIQUE: X-RAY POWDER DIFFRACTION SAMPLE: 1 g to 10 g ANALYTE: Chrysotile SHIPMENT: Seal securely to prevent escape of asbestos PREPARATION: Grind under liquid nitrogen; wet-sieve SAMPLE through 10 µm sieve STABILITY: Indefinitely DEPOSIT: 5 mg dust on 0.45 µm silver membrane BLANKS: None required filter ACCURACY XRD: Copper target X-ray tube; optimize for intensity; 1° slit; integrated intensity with RANGE STUDIED: 1% to 100% in talc [1] background subtraction BIAS: Negligible if standards and samples are CALIBRATION: Suspensions of asbestos in 2-propanol matched in particle size [1] RANGE: 1% to 100% asbestos OVERALL PRECISION ( ): Unknown; depends on matrix and ESTIMATED LOD: 0.2% asbestos in talc and calcite; 0.4% concentration asbestos in heavy X-ray absorbers such as ferric oxide ACCURACY: ±14% to ±25% PRECISION ( ): 0.07 (5% to 100% asbestos); 0.10 (@ 3% asbestos); 0.125 (@ 1% asbestos) APPLICABILITY: Analysis of percent chrysotile asbestos in bulk samples. INTERFERENCES: Antigorite (massive serpentine), chlorite, kaolinite, bementite, and brushite interfere. X-ray fluorescence and absorption is a problem with some elements; fluorescence can be circumvented with a diffracted beam monochromator, and absorption is corrected for in this method. OTHER METHODS: This is NIOSH method P&CAM 309 [2] applied to bulk samples only, since the sensitivity is not adequate for personal air samples. -
State County Historic Site Name As Reported Development Latitude
asbestos_sites.xls. Summary of information of reported natural occurrences of asbestos found in geologic references examined by the authors. Dataset is part of: Van Gosen, B.S., and Clinkenbeard, J.P., 2011, Reported historic asbestos mines, historic asbestos prospects, and other natural occurrences of asbestos in California: U.S. Geological Survey Open-File Report 2011-1188, available at http://pubs.usgs.gov/of/2011/1188/. Data fields: State, ―CA‖ indicates that the site occurs in California. County, Name of the county in which the site is located. Historic site name as reported, The name of the former asbestos mine, former asbestos prospect, or reported occurrence, matching the nomenclature used in the source literature. Development, This field indicates whether the asbestos site is a former asbestos mine, former prospect, or an occurrence. "Past producer" indicates that the deposit was mined and produced asbestos ore for commercial uses sometime in the past. "Past prospect" indicates that the asbestos deposit was once prospected (evaluated) for possible commercial use, typically by trenching and (or) drilling, but the deposit was not further developed. "Occurrence" indicates that asbestos was reported at this site. The occurrence category includes (1) sites where asbestos-bearing rock is described in a geologic map or report and (2) asbestos noted as an accessory mineral or vein deposit within another type of mineral deposit. Latitude, The latitude of the site's location in decimal degrees, measured using the North American Datum of -
Iron.Rich Amesite from the Lake Asbestos Mine. Black
Canodian Mineralogist Yol.22, pp. 43742 (1984) IRON.RICHAMESITE FROM THE LAKE ASBESTOS MINE. BLACKLAKE. OUEBEC MEHMET YEYZT TANER,* AND ROGER LAURENT DAporternentde Gdologie,Universitd Loval, Qudbec,Qudbec GIK 7P4 ABSTRACT o 90.02(1l)', P W.42(12)',1 89.96(8)'.A notreconnais- sance,c'est la premibrefois qu'on ddcritune am6site riche Iron-rich amesite is found in a metasomatically altered enfer. Elles'ct form€ependant l'altdration hydrothermale granite sheet20 to 40 cm thick emplacedin serpentinite of du granitedans la serpentinite,dans les m€mes conditions the Thetford Mi[es ophiolite complex at the Lake Asbestos debasses pression et temperaturequi ont prdsid6d la for- mine (z16o01'N,11"22' W) ntheQuebec Appalachians.The mation de la rodingite dansle granite et de I'amiante- amesiteis associatedsdth 4lodingife 6semblage(grossu- chrysotiledans la serpentinite. lar + calcite t diopside t clinozoisite) that has replaced the primary minerals of the granite. The Quebec amesite Mots-clds:am6site, rodingite, granite, complexeophio- occurs as subhedral grains 2@ to 6@ pm.in diameter that litique, Thetford Mines, Qu6bec. have a tabular habit. It is optically positive with a small 2V, a 1.612,1 1.630,(t -'o = 0.018).Its structuralfor- INTRoDUc"iloN mula, calculated from electron-microprobe data, is: (Mg1.1Fe6.eA1s.e)(Alo.esil.df Os(OH)r.2. X-ray powder- Amesite is a raxehydrated aluminosilicate of mag- diffraction yield data dvalues that are systematicallygreater nesium in which some ferrous iron usually is found than those of amesitefrom Chester, Massachusetts,prob- replacingmapesium. The extent of this replacement ably becauseof the partial replacement of Mg by Fe. -
Zincite (Zn, Mn2+)O
Zincite (Zn, Mn2+)O c 2001-2005 Mineral Data Publishing, version 1 Crystal Data: Hexagonal. Point Group: 6mm. Crystals rare, typically pyramidal, hemimorphic, with large {0001}, to 2.5 cm, rarely curved; in broad cleavages, foliated, granular, compact, massive. Twinning: On {0001}, with composition plane {0001}. Physical Properties: Cleavage: {1010}, perfect; parting on {0001}, commonly distinct. Fracture: Conchoidal. Tenacity: Brittle. Hardness = 4 VHN = 205–221 (100 g load). D(meas.) = 5.66(2) D(calc.) = 5.6730 Rare pale yellow fluorescence under LW UV. Optical Properties: Translucent, transparent in thin fragments. Color: Yellow-orange to deep red, rarely yellow, green, colorless; deep red to yellow in transmitted light; light rose-brown in reflected light, with strong red to yellow internal reflections. Streak: Yellow-orange. Luster: Subadamantine to resinous. Optical Class: Uniaxial (+). ω = 2.013 = 2.029 R1–R2: (400) 13.0–13.6, (420) 12.8–13.2, (440) 12.6–12.8, (460) 12.3–12.6, (480) 12.1–12.4, (500) 12.0–12.2, (520) 11.8–12.1, (540) 11.8–12.0, (560) 11.7–11.9, (580) 11.6–11.8, (600) 11.4–11.7, (620) 11.3–11.6, (640) 11.2–11.5, (660) 11.1–11.4, (680) 11.0–11.2, (700) 11.0–11.2 Cell Data: Space Group: P 63mc (synthetic). a = 3.24992(5) c = 5.20658(8) Z = 2 X-ray Powder Pattern: Synthetic. 2.476 (100), 2.816 (71), 2.602 (56), 1.626 (40), 1.477 (35), 1.911 (29), 1.379 (28) Chemistry: (1) (2) SiO2 0.08 FeO 0.01 0.23 MnO 0.27 0.29 ZnO 99.63 98.88 Total 99.99 [99.40] (1) Sterling Hill, New Jersey, USA. -
Chrysotile Asbestos
This report contains the collective views of an international group of experts and does not necessarily represent the decisions or the stated policy of the United Nations Environment Programme, the International Labour Organisation, or the World Health Organization. Environmental Health Criteria 203 CHRYSOTILE ASBESTOS First draft prepared by Dr G. Gibbs, Canada (Chapter 2), Mr B.J. Pigg, USA (Chapter 3), Professor W.J. Nicholson, USA (Chapter 4), Dr A. Morgan, UK and Professor M. Lippmann, USA (Chapter 5), Dr J.M.G. Davis, UK and Professor B.T. Mossman, USA (Chapter 6), Professor J.C. McDonald, UK, Professor P.J. Landrigan, USA and Professor W.J. Nicholson, USA (ChapterT), Professor H. Schreier, Canada (Chapter 8). Published under the joint sponsorship of the United Nations Environment Progralnme, the International Labour Organisation, and the World Health Organization, and produced within the framework of the Inter-Organization Programme for the Sound Management of Chemicals. World Health Organization Geneva, 1998 The International Programme on chemicat safety (Ipcs), esrablished in 1980, is a joint venture of the united Nations Environment programme (uNEp), the International l-abour organisation (ILo), and the world ueatttr orginization (WHO). The overall objectives of the IPCS are to establish the scientific basis for assessment of the risk to human health and the environment from exposure rc chemicals, through international peer review processes, as a prerequisiie for the promotion of chemical safety, and to provide technical assistance -
Chrysotile Asbestos As a Cause of Mesothelioma: Application of the Hill Causation Model
Commentary Chrysotile Asbestos as a Cause of Mesothelioma: Application of the Hill Causation Model RICHARD A. LEMEN, PHD Chrysotile comprises over 95% of the asbestos used this method, researchers are asked to evaluate nine today. Some have contended that the majority of areas of consideration: strength of association, tempo- asbestos-related diseases have resulted from exposures rality, biologic gradient, consistency, specificity, bio- to the amphiboles. In fact, chrysotile is being touted as logic plausibility, coherence, experimental evidence, the form of asbestos which can be used safely. Causa- and analogy. None of these considerations, in and of tion is a controversial issue for the epidemiologist. How itself, is determinative for establishing a causal rela- much proof is needed before causation can be estab- tionship. As Hill himself noted, “[n]one of my nine lished? This paper examines one proposed model for establishing causation as presented by Sir Austin Brad- view points can bring indisputable evidence for or ford Hill in 1965. Many policymakers have relied upon against the cause and effect hypothesis, and none can this model in forming public health policy as well as be required as a sine qua non.” In the same vein, it is deciding litigation issues. Chrysotile asbestos meets not necessary for all nine considerations to be met Hill’s nine proposed criteria, establishing chrysotile before causation is established. Instead, Hill empha- asbestos as a cause of mesothelioma. Key words: sized that the responsibility for making causal judg- asbestos; chrysotile; amphiboles; causation; mesothe- ments rested with a scientific evaluation of the totality lioma; Hill model. of the data. -
List of Abbreviations
List of Abbreviations Ab albite Cbz chabazite Fa fayalite Acm acmite Cc chalcocite Fac ferroactinolite Act actinolite Ccl chrysocolla Fcp ferrocarpholite Adr andradite Ccn cancrinite Fed ferroedenite Agt aegirine-augite Ccp chalcopyrite Flt fluorite Ak akermanite Cel celadonite Fo forsterite Alm almandine Cen clinoenstatite Fpa ferropargasite Aln allanite Cfs clinoferrosilite Fs ferrosilite ( ortho) Als aluminosilicate Chl chlorite Fst fassite Am amphibole Chn chondrodite Fts ferrotscher- An anorthite Chr chromite makite And andalusite Chu clinohumite Gbs gibbsite Anh anhydrite Cld chloritoid Ged gedrite Ank ankerite Cls celestite Gh gehlenite Anl analcite Cp carpholite Gln glaucophane Ann annite Cpx Ca clinopyroxene Glt glauconite Ant anatase Crd cordierite Gn galena Ap apatite ern carnegieite Gp gypsum Apo apophyllite Crn corundum Gr graphite Apy arsenopyrite Crs cristroballite Grs grossular Arf arfvedsonite Cs coesite Grt garnet Arg aragonite Cst cassiterite Gru grunerite Atg antigorite Ctl chrysotile Gt goethite Ath anthophyllite Cum cummingtonite Hbl hornblende Aug augite Cv covellite He hercynite Ax axinite Czo clinozoisite Hd hedenbergite Bhm boehmite Dg diginite Hem hematite Bn bornite Di diopside Hl halite Brc brucite Dia diamond Hs hastingsite Brk brookite Dol dolomite Hu humite Brl beryl Drv dravite Hul heulandite Brt barite Dsp diaspore Hyn haiiyne Bst bustamite Eck eckermannite Ill illite Bt biotite Ed edenite Ilm ilmenite Cal calcite Elb elbaite Jd jadeite Cam Ca clinoamphi- En enstatite ( ortho) Jh johannsenite bole Ep epidote -
A Study on Optical Properties of Zinc Silicate Glass-Ceramics As a Host for Green Phosphor
applied sciences Article A Study on Optical Properties of Zinc Silicate Glass-Ceramics as a Host for Green Phosphor Siti Aisyah Abdul Wahab 1, Khamirul Amin Matori 1,2,*, Mohd Hafiz Mohd Zaid 1,2, Mohd Mustafa Awang Kechik 2 , Sidek Hj Ab Aziz 2, Rosnita A. Talib 3, Aisyah Zakiah Khirel Azman 1, Rahayu Emilia Mohamed Khaidir 1, Mohammad Zulhasif Ahmad Khiri 1 and Nuraidayani Effendy 2 1 Materials Synthesis and Characterization Laboratory, Institute of Advanced Technology, Universiti Putra Malaysia, UPM Serdang, Selangor 43400, Malaysia; [email protected] (S.A.A.W.); [email protected] (M.H.M.Z.); [email protected] (A.Z.K.A.); [email protected] (R.E.M.K.); [email protected] (M.Z.A.K.) 2 Department of Physics, Faculty of Science, Universiti Putra Malaysia, UPM Serdang, Selangor 43400, Malaysia; [email protected] (M.M.A.K.); [email protected] (S.H.A.A.); aidayanieff[email protected] (N.E.) 3 Department of Process and Food Engineering, Faculty of Engineering, Universiti Putra Malaysia, UPM Serdang, Selangor 43400, Malaysia; [email protected] * Correspondence: [email protected]; Tel.: +6016-267-3321 Received: 13 April 2020; Accepted: 6 May 2020; Published: 18 July 2020 Abstract: For the very first time, a study on the crystallization growth of zinc silicate glass and glass-ceramics was done, in which white rice husk ash (WRHA) was used as the silicon source. In this study, zinc silicate glass was fabricated by using melt–quenching methods based on the composition (ZnO)0.55(WRHA)0.45, where zinc oxide (ZnO) and white rice husk ash were used as the raw materials. -
Nepouite Isomorphous Series
N¶epouite Ni3Si2O5(OH)4 c 2001 Mineral Data Publishing, version 1.2 ° Crystal Data: Orthorhombic, probable. Point Group: n.d. As crude pseudohexagonal vermiform crystals, to 1 cm; massive. Physical Properties: Hardness = 2.5 D(meas.) = 3.24 D(calc.) = [3.07{3.40] Optical Properties: Semitransparent. Color: Intense dark green to dull green. Optical Class: Biaxial ({). Pleochroism: Weak; X = dark green; Z = yellow-green. ® = 1.622 ¯ = 1.576{1.579 ° = 1.645 2V(meas.) = n.d. Cell Data: Space Group: n.d. a = 5.27{5.31 b = 9.14{9.20 c = 7.24{7.28 Z = [2] X-ray Powder Pattern: Letovice, Czech Republic. 7.31 (100), 3.63 (90), 2.501 (70), 2.894 (60), 1.530 (60), 4.55 (50b), 2.321 (40) Chemistry: (1) (2) (3) SiO2 32.84 37.0 31.60 Al2O3 0.97 0.21 Fe2O3 0.22 FeO 1.90 NiO 49.05 44.9 58.92 MgO 3.64 5.95 CaO 0.50 0.22 Na2O 0.10 K2O 0.07 + H2O 9.64 11.9 9.48 Total 98.54 100.6 100.00 (1) N¶epoui, New Caledonia. (2) Nakety, New Caledonia. (3) Ni3Si2O5(OH)4: Polymorphism & Series: Dimorphous with pecoraite; forms a series with lizardite. Mineral Group: Kaolinite-serpentine group. Occurrence: An alteration product of nickel-rich ultrama¯c rocks. Association: Serpentine, chlorite, hydrous nickel silicates, iron oxides. Distribution: From the Reis II mine, N¶epoui; near Nakety, and at Thio, New Caledonia. In the 132 North nickel mine, Widgiemooltha district, Western Australia. From Pavlos, Greece. -
Does Low Exposure to Chrysotile Pose a Health Risk?
Does Low Exposure to Chrysotile Pose a Health Risk? Dr. Tom Hesterberg Principal Toxicologist Center for Toxicology and Environmental Health American Conference Institute’s Asbestos Claims and Litigation January 30-31, 2014 San Francisco, California 5120 North Shore Drive | North Little Rock, AR 72118 | Main Line: 501.801.8500 Overview of Fiber Toxicology Studies • Basics of Fiber Toxicology • Chromosomal Effects • Fiber Biopersistence • Rodent Inhalation Studies • Thresholds for Fiber Toxicity 2 Basics of Fiber Toxicology 3 Dose The Cornerstone of Toxicology “All substances are poisons; there is none which is not a poison. The right dose differentiates a poison from a remedy.” Paracelsus (1493-1541). 4 Definition of Threshold The dose below which a given effect is not observed A threshold is a result of our bodies’ protective mechanisms 5 Doses of Common Substances Substance Normal Lethal Water 1.5 qts 15 qts Aspirin 2 tablets 90 tablets Table Salt 3 tsp. 60 tsp. Cyanide in Lima Beans 0.5 cups 11 cups Toxicity is the adverse effect caused when a chemical reaches a sufficient dose—threshold. 6 Asbestos Types Chrysotile Asbestos Crocidolite Asbestos The Three Ds of Fiber Toxicology Dose - Amount reaching the deep lung Dimension - Thin fibers deposit in the deep lung; long fibers are more toxic Durability - Dissolution and breakage; more durable fibers are more toxic Hesterberg and Hart., Inhal. Tox., 2001 8 Biopersistence Determines Toxic Potential of Fibers Long Fiber (> 20 µm) Incongruent Dissolution Congruent Dissolution Transverse Breakage Complete Altered Biological Translocation Dissolution Reactivity Macrophage Uptake Mucociliary Clearance Epithelial Cell Uptake Intracellular Degradation Translocation to Interstitium Hesterberg and Hart., Inhal. -
Coprecipitation of Co2+, Ni2+ and Zn2+ with Mn(III/IV) Oxides Formed in Metal-Rich Mine Waters
Article Coprecipitation of Co2+, Ni2+ and Zn2+ with Mn(III/IV) Oxides Formed in Metal-Rich Mine Waters Javier Sánchez-España 1,* and Iñaki Yusta 2 1 Area of Geochemistry and Sustainable Mining, Department of Geological Resources Research, Spanish Geological Survey (IGME), Calera 1, Tres Cantos, 28760 Madrid, Spain 2 Department of Mineralogy and Petrology, University of the Basque Country (UPV/EHU), Faculty of Science and Technology, Apdo. 644, 48080 Bilbao, Spain; [email protected] * Correspondence: [email protected] Received: 19 February 2019; Accepted: 6 April 2019; Published: 10 April 2019 Abstract: Manganese oxides are widespread in soils and natural waters, and their capacity to adsorb different trace metals such as Co, Ni, or Zn is well known. In this study, we aimed to compare the extent of trace metal coprecipitation in different Mn oxides formed during Mn(II) oxidation in highly concentrated, metal-rich mine waters. For this purpose, mine water samples collected from the deepest part of several acidic pit lakes in Spain (pH 2.7–4.2), with very high concentration of manganese (358–892 mg/L Mn) and trace metals (e.g., 795–10,394 µg/L Ni, 678–11,081 µg/L Co, 259– 624 mg/L Zn), were neutralized to pH 8.0 in the laboratory and later used for Mn(II) oxidation experiments. These waters were subsequently allowed to oxidize at room temperature and pH = 8.5–9.0 over several weeks until Mn(II) was totally oxidized and a dense layer of manganese precipitates had been formed. These solids were characterized by different techniques for investigating the mineral phases formed and the amount of coprecipitated trace metals. -
Hardystonite from the Desert View Mine, California
Bucknell University Bucknell Digital Commons Faculty Journal Articles Faculty Scholarship Spring 2014 Hardystonite From the Desert View Mine, California James A. Van Fleet Bucknell University, [email protected] Earl R. Verbeek Sterling Hill Mining Museum Follow this and additional works at: https://digitalcommons.bucknell.edu/fac_journ Part of the Geology Commons Recommended Citation Van Fleet, James A. and Verbeek, Earl R.. "Hardystonite From the Desert View Mine, California." The Picking Table: Journal of the Franklin-Ogdensburg Mineralogical Society (2014) : 15-17. This Article is brought to you for free and open access by the Faculty Scholarship at Bucknell Digital Commons. It has been accepted for inclusion in Faculty Journal Articles by an authorized administrator of Bucknell Digital Commons. For more information, please contact [email protected]. Hardystonite From the Desert View Mine, California EARL R. VERBEEK, PhD RESIDENT GEOLOGIST, STERLING HILL MINING MUSEUM 30 PLANT STREET, OGDENSBURG, NJ 07439 [email protected] JAMES VAN FLEET 222 MARKET STREET MIFFLINBURG, PA 17844 [email protected] INTRODUCTION View Mine and further strengthen its mineralogical similarities to Franklin. Although much of the original geology has been In late December of 2012, Kevin Brady, an accomplished obliterated by intrusion of the granodiorite, Leavens and Patton and knowledgeable field collector of minerals, sent to one of (2008) provided mineralogical and geochemical evidence that us (ERV) a specimen of an unknown mineral that he noted the Desert View deposit, like that at Franklin, is exhalative, fluoresced deep violet under shortwave (SW) ultraviolet light and that it is genetically intermediate between the Franklin- and thus resembled hardystonite.