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isPermaLink="false">http://www.vikanemonitor.com/index2.php/?p=95</guid> <description><![CDATA[<p>From the National Library of Medicine&#8217;s Hazardous Substance Databank SULFURYL FLUORIDECASRN: 2699-79-8 See Occupational Exposure Standards Human Health Effects: Human Toxicity Excerpts: Accidental human exposure caused nausea, vomiting, cramps, itching. [Lewis, R.J. Sax&#8217;s Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY:&#8230; <a
class="more-link" href="http://www.vikanemonitor.com/sulfuryl-fluoride-toxicology/">Continue reading <span
class="meta-nav">&#8594;</span></a></p> ]]></description> <content:encoded><![CDATA[<h5><strong><br
/>From the National Library of Medicine&#8217;s <a
href="http://toxnet.nlm.nih.gov/index.html" target="_blank">Hazardous Substance Databank</a></strong></h5><p><span
style="color: navy; font-size: 8pt;"> <strong>SULFURYL FLUORIDE</strong></span><br
/>CASRN: 2699-79-8</p><p>See <a
href="#occ1">Occupational Exposure Standards</a></p><p><span
style="font-size: 8pt;"><strong>Human Health Effects:</strong></span></p><p><strong>Human Toxicity Excerpts:</strong></p><p>Accidental human exposure caused nausea, vomiting, cramps, itching. <br
/>[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996., p. 3050]**PEER REVIEWED**</p><p><span
id="more-95"></span>A case attributed to <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>involved a 30 yr old man who was exposed for about 4 hr to unknown concentrations of a 99:1 mixture of it with chloropicrin. While still at work, he experienced nausea, vomiting, crampy abdominal pain, and itching. When admitted to /the/ hospital soon afterward, vital signs were normal; the only abnormalities observed were reddening of the conjunctival, pharyngeal, and nasal mucosae; diffuse rhonchi; and paresthesia of the lateral surface of the right leg. The serum was positive for fluoride. The signs and symptoms resolved quickly; the patient was discharged on the fourth hospital day. He returned three times as an outpatient, complaining of persistent scratching of the throat, flatulence, and difficulty in reading. Ophthalmological examination revealed no abnormality, and the patient was discharged with a strong suspicion that emotional factors played a significant role in his disorder. <br
/>[Hayes, W.J., Jr., E.R. Laws, Jr., (eds.). Handbook of Pesticide Toxicology. Volume 2. Classes of Pesticides. New York, NY: Academic Press, Inc., 1991., p. 564]**PEER REVIEWED**</p><p>A 25 year old man with postmortem blood alcohol level of 0.156% was found lifeless in a residence that had been fumigated with <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>under canvas. <br
/>[Hayes, W.J., Jr., E.R. Laws, Jr., (eds.). Handbook of Pesticide Toxicology. Volume 2. Classes of Pesticides. New York, NY: Academic Press, Inc., 1991., p. 564]**PEER REVIEWED**</p><p>Caution: Potential symptoms of overexposure are conjunctivitis, rhinorrhea and pharyngitis; paresthesia. <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p>Two fatalities occurred when the owners of a home re-entered after the dwelling had been fumigated with 250 pounds of <span
style="color: red;"><strong>sulfuryl fluoride. </strong></span>The concentration to which the occupants were exposed was not determined. The man died within 24 hr, and the woman expired 6 days after exposure. Signs of intoxication included severe dyspnea, cough, generalized seizure, cardiopulmonary arrest (in the male), and weakness, anorexia, nausea, repeated vomiting, and hypoxemia; ventricular fibrillation and diffuse pulmonary infiltration were also reported in the female. <br
/>[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I, II, III. Cincinnati, OH: ACGIH, 1991., p. 1471]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Skin, Eye and Respiratory Irritations:</strong></p><p>HIGHLY IRRITATING TO RESPIRATORY TRACT. <br
/>[Budavari, S. (ed.). The Merck Index - Encyclopedia of Chemicals, Drugs and Biologicals. Rahway, NJ: Merck and Co., Inc., 1989., p. 1419]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Drug Warnings:</strong></p><p>Food and Environmental Agents: Effect on Breast-Feeding: Reported Sign or Symptom in Infant or Effect on Lactation: Fluorides: None. /from Table 7/ <br
/>[Report of the American Academy of Pediatrics Committee on Drugs in Pediatrics 93 (1): 142 (1994)]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Medical Surveillance:</strong></p><p>Consider the points of attack /respiratory system, central nervous system/ in preplacement and periodic physical examination. <br
/>[Sittig, M. Handbook of Toxic and Hazardous Chemicals and Carcinogens, 1985. 2nd ed. Park Ridge, NJ: Noyes Data Corporation, 1985., p. 820]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Probable Routes of Human Exposure:</strong></p><p>Inhalation, eye and skin contact <br
/>[Sittig, M. Handbook of Toxic and Hazardous Chemicals and Carcinogens, 1985. 2nd ed. Park Ridge, NJ: Noyes Data Corporation, 1985., p. 820]**PEER REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Emergency Medical Treatment:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>Emergency Medical Treatment:</strong></p><table
style="width: 600px;" align="center"><tbody><tr><td
valign="top"><strong>EMT Copyright Disclaimer:</strong></td></tr><tr><td
align="left"><p>Portions of the POISINDEX(R) and MEDITEXT(R) database have been provided here for general reference. THE COMPLETE POISINDEX(R) DATABASE OR MEDITEXT(R) DATABASE SHOULD BE CONSULTED FOR ASSISTANCE IN THE DIAGNOSIS OR TREATMENT OF SPECIFIC CASES. The use of the POISINDEX(R) and MEDITEXT(R) databases is at your sole risk.</p><p>The POISINDEX(R) and MEDITEXT(R) databases are provided &#8220;AS IS&#8221; and &#8220;as available&#8221; for use, without warranties of any kind, either expressed or implied. Micromedex makes no representation or warranty as to the accuracy, reliability, timeliness, usefulness or completeness of any of the information contained in the POISINDEX(R) and MEDITEXT(R) databases.</p><p>ALL IMPLIED WARRANTIES OF MERCHANTABILITY AND FITNESS FOR A PARTICULAR PURPOSE OR USE ARE HEREBY EXCLUDED. Micromedex does not assume any responsibility or risk for your use of the POISINDEX(R) or MEDITEXT(R) databases. Copyright 1974-2006 Thomson MICROMEDEX. All Rights Reserved. Any duplication, replication, &#8220;downloading,&#8221; sale, redistribution or other use for commercial purposes is a violation of Micromedex&#8217; rights and is strictly prohibited.</p><p>The following Overview, *** <span
style="color: red;"><strong>SULFURYL FLUORIDE ***, </strong></span>is relevant for this HSDB record chemical.</p></td></tr><tr><td
valign="top"><strong>Life Support:</strong></td></tr><tr><td
align="left">o This overview assumes that basic life support measures have been instituted.</td></tr><tr><td
valign="top"><strong>Clinical Effects:</strong></td></tr><tr><td
align="left"><p>0.2.1 SUMMARY OF EXPOSURE</p><p>0.2.1.1 ACUTE EXPOSURE</p><p>A) INHALATION &#8211; <span
style="color: red;"><strong>Sulfuryl fluoride </strong></span>is heavier than air and prolonged breathing may result in fatal hypoxia. Nose, throat, and respiratory tract irritation may occur. Death has resulted from pulmonary edema and respiratory arrest following inhalation exposure.</p><p>B) TOPICAL &#8211; Contact with escaping liquefied gas may cause frostbite injury. Eye irritation may occur with direct corneal contact.</p><p>C) Paresthesias or seizures may develop. Nausea, vomiting, abdominal pain, diffuse rhonchi, hypotension, carpopedal spasm, dysrhythmias, and pruritus may occur.</p><p>D) EXPERIMENTAL ANIMALS &#8211; In experimental animals CNS depression, tremors, seizures, pulmonary edema, and liver and kidney injury have been reported.</p><p>0.2.5 CARDIOVASCULAR 0.2.5.1 ACUTE EXPOSURE A) Cardiac dysrhythmias and hypotension may develop in patients with patients with severe poisoning.</p><p>0.2.6 RESPIRATORY 0.2.6.1 ACUTE EXPOSURE A) Dyspnea, irritation, and pulmonary edema can occur.</p><p>0.2.7 NEUROLOGIC 0.2.7.1 ACUTE EXPOSURE A) Weakness, restlessness, seizures, and CNS depression may occur. Long-term exposure may be associated with olfactory deficits and subclinical CNS effects.</p><p>0.2.8 GASTROINTESTINAL 0.2.8.1 ACUTE EXPOSURE A) Nausea, vomiting, drooling, and fecal incontinence may occur following acute ingestion exposure.</p><p>0.2.20 REPRODUCTIVE HAZARDS A) Inhalation exposure to <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>was not teratogenic or embryotoxic in rats or rabbits.</p><p>0.2.21 CARCINOGENICITY 0.2.21.1 IARC CATEGORY A) IARC Carcinogenicity Ratings for CAS2699-79-8 (IARC, 2004): 1) Not Listed</p></td></tr><tr><td
valign="top"><strong>Laboratory:</strong></td></tr><tr><td
align="left"><p>A) Serum fluoride and calcium levels may be useful following ingestion or significant inhalation exposure.</p><p>B) A number of chemicals produce abnormalities of the hematopoietic system, liver, and kidneys. Monitoring complete blood count, urinalysis, and liver and kidney function tests is suggested for patients with significant exposure.</p><p>C) If respiratory tract irritation or respiratory depression is evident, monitor arterial blood gases, chest x-ray, and pulmonary function tests.</p></td></tr><tr><td
valign="top"><strong>Treatment Overview:</strong></td></tr><tr><td
align="left"><p>0.4.3 INHALATION EXPOSURE</p><p>A) INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with inhaled beta2 agonist and oral or parenteral corticosteroids.</p><p>B) Endotracheal intubation, supplemental oxygenation, and assisted ventilation may be required. Calcium replacement therapy may be needed.</p><p>C) ACUTE LUNG INJURY: Maintain ventilation and oxygenation and evaluate with frequent arterial blood gas or pulse oximetry monitoring. Early use of PEEP and mechanical ventilation may be needed.</p><p>D) SEIZURES: Administer a benzodiazepine IV; DIAZEPAM (ADULT: 5 to 10 mg, repeat every 10 to 15 min as needed. CHILD: 0.2 to 0.5 mg/kg, repeat every 5 min as needed) or LORAZEPAM (ADULT: 2 to 4 mg; CHILD: 0.05 to 0.1 mg/kg). 1) Consider phenobarbital if seizures recur after diazepam 30 mg (adults) or 10 mg (children &gt; 5 years). 2) Monitor for hypotension, dysrhythmias, respiratory depression, and need for endotracheal intubation. Evaluate for hypoglycemia, electrolyte disturbances, hypoxia.</p><p>E) Carefully observe patients with inhalation exposure for the development of any systemic signs or symptoms and administer symptomatic treatment as necessary.</p><p>F) TORSADES DE POINTES: Hemodynamically unstable patients require electrical cardioversion. Treat stable patients with magnesium, isoproterenol, and/or atrial overdrive pacing. Correct electrolyte abnormalities (hypomagnesemia, hypokalemia, hypocalcemia).</p><p>1) MAGNESIUM SULFATE/DOSE: ADULTS: 2 g IV over 1 to 2 min, repeat 2 g bolus and begin infusion of 0.5 to 1 g/hr if dysrhythmias recur. CHILDREN: 25 to 50 mg/kg diluted to 10 mg/mL; infuse IV over 5 to 15 min.</p><p>2) ISOPROTERENOL/DOSE: Correct hypovolemia first. ADULT: 2 to 10 mcg/minute (CHILD: 0.1 to 1 mcg/kg/minute) IV infusion; titrate to heart rate and rhythm response. Mix 1 mg isoproterenol HCl in 500 mL D5W for a 2 mcg/mL solution.</p><p>3) OVERDRIVE PACING: Begin at 130 to 150 beats per min, decrease as tolerated. 4) Avoid class Ia (quinidine, disopyramide, procainamide, aprindine) and most class III antidysrhythmics (N-acetylprocainamide, sotalol).</p><p>0.4.4 EYE EXPOSURE A) DECONTAMINATION: Irrigate exposed eyes with copious amounts of room temperature water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist, the patient should be seen in a health care facility.</p><p>0.4.5 DERMAL EXPOSURE A) OVERVIEW 1) Rewarming and a variety of topical treatments have been recommended for treating frostbite injuries (See Main Section).</p></td></tr><tr><td
valign="top"><strong>Range of Toxicity:</strong></td></tr><tr><td
align="left">A) Two fatalities occurred in a couple who lived in an 80,000 cubic foot house fumigated with 250 pounds of <span
style="color: red;"><strong>sulfuryl fluoride. </strong></span>Following fumigation, no one should enter the area without a self-contained breathing apparatus until measured air concentrations are below 5 ppm.</td></tr></tbody></table><p>[Rumack BH POISINDEX(R) Information System Micromedex, Inc., Englewood, CO, 2006; CCIS Volume 129, edition expires Aug, 2006. Hall AH &amp; Rumack BH (Eds): TOMES(R) Information System Micromedex, Inc., Englewood, CO, 2006; CCIS Volume 129, edition expires Aug, 2006., p. ]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Antidote and Emergency Treatment:</strong></p><p>For immediate first aid: Ensure that adequate decontamination has been carried out. If victim is not breathing, start artificial respiration, preferably with a demand-valve resuscitator, bag-valve-mask device, or pocket mask as trained. Perform CPR if necessary. Immediately flush contaminated eyes with gently flowing water. Do not induce vomiting. If vomiting occurs, lean patient forward or place on left side (head-down position, if possible) to maintain an open airway and prevent aspiration. Keep victim quiet and maintain normal body temperature. Obtain medical attention. /Fluorine and related compounds/ <br
/>[Bronstein, A.C., P.L. Currance; Emergency Care for Hazardous Materials Exposure. 2nd ed. St. Louis, MO. Mosby Lifeline. 1994., p. 416]**PEER REVIEWED**</p><p>For basic treatment: Establish a patent airway. Suction if necessary. Watch for signs of respiratory insufficiency and assist ventilations if necessary. Administer oxygen by nonrebreather mask at 10 to 15 L/min. Monitor for pulmonary edema and treat if necessary &#8230; Monitor for shock and treat if necessary &#8230; Anticipate seizures and treat if necessary &#8230; For eye contamination, flush eyes immediately with water. Irrigate each eye continuously with normal saline during transport &#8230; Do not use emetics. For ingestion, rinse mouth and administer 5 mL/kg up to 200 mL of water for dilution if the patient can swallow, has a strong gag reflex, and does not drool. &#8230; Cover skin burns with sterile dressings after decontamination &#8230; . /Fluorine and related compounds/ <br
/>[Bronstein, A.C., P.L. Currance; Emergency Care for Hazardous Materials Exposure. 2nd ed. St. Louis, MO. Mosby Lifeline. 1994., p. 416]**PEER REVIEWED**</p><p>Treatment /of acute poisoning/ includes the iv admin of glucose in saline and gastric lavage with lime water (0.15% calcium hydroxide soln) or other Ca+2 salts to precipitate the fluoride. Calcium gluconate is given iv for tetany; urine volume is kept high with vigorous fluid resuscitation. /Fluoride/ <br
/>[Hardman, J.G., L.E. Limbird, P.B. Molinoff, R.W. Ruddon, A.G. Goodman (eds.). Goodman and Gilman's The Pharmacological Basis of Therapeutics. 9th ed. New York, NY: McGraw-Hill, 1996., p. 1538]**PEER REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Animal Toxicity Studies:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>Non-Human Toxicity Excerpts:</strong></p><p>TEST ANIMALS TOLERATED 100 PPM FOR 7 HR/DAY, 5 DAYS/WK FOR 6 MO. <br
/>[Spencer, E.Y. Guide to the Chemicals Used in Crop Protection. 6th ed. Publication 1093, Research Institute, Agriculture Canada, Ottawa, Canada: Information Canada, 1973., p. 476]**PEER REVIEWED**</p><p>ORCHID PLANTS &amp; A GRAPEFRUIT TREE SUFFERED CONSIDERABLE DAMAGE WHEN <span
style="color: red;"><strong>VIKANE</strong></span> (SO2F2) WAS USED TO FUMIGATE A TERMITE-RIDDEN HOUSE 15-30 FT AWAY. ORCHIDS DEVELOPED BLACK ROT &amp; LEAF TIP ROT AFTER 1 WK, &amp; THE TREE LOST ITS LEAVES &amp; FRUIT AFTER 4 DAYS. <br
/>[MORTON M, MORTON H; AM ORCHID SOC BULL 43 (10): 890 (1974)]**PEER REVIEWED**</p><p>Using quadrupole mass spectrometric analysis of sparked (electrical discharge) sulfur hexafluoride over energy and pressure ranges of 4-94 KJ and 40-233 kPa, respectively, the by-products included SOF2, SO2F3, SF4, SOF4, SiF4, SO2, and HF. One mixture containing 0.2% SO2F2 and SiF4, 2% SOF2, and 4% HF was only weakly cytotoxic to Chinese hamster lung cells, exhibiting approx 20% of the cytotoxic activity of sparked SF6. <br
/>[Griffin GD et al; Gaseous Dielectr Proc Int Symp 4th: 261-75 (1984)]**PEER REVIEWED**</p><p>Lab experiments showed that <span
style="color: red;"><strong>Vikane</strong></span> was effective against small groups of the Formosan termite exposed to the gas directly at 20-40 deg C. Very high or total mortality was observed above 20 deg C at concn of 5 ml/3.8 l. At 30 deg C, penetration was sufficient to produce high mortality with gas concn of 4 ml/3.8 l. <br
/>[LaFage JP et al; Down Earth 39 (1): 27-32 (1983)]**PEER REVIEWED**</p><p>The inhalation toxicity of the structural fumigant <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>was evaluated in male and female New Zealand White rabbits. Exposures during the preliminary 2-wk study were 6 hr/day, 5 day/wk, to 0, 100, 300, or 600 ppm <span
style="color: red;"><strong>sulfuryl fluoride. </strong></span>Rabbits exposed to 600 ppm <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>were hyperactive; one animal had a few convulsion. Exposure to 300 or 600 ppm for 2 wk resulted in vacuolation and/or malacia in the cerebrum of all rabbits and most of these rabbits also had moderate inflammation of nasal tissues; rabbits at 600 ppm had inflammed tracheas or bronchi. A subsequent 13 wk study evaluated rabbits exposed to 0, 30, 100, or 337 ppm <span
style="color: red;"><strong>sulfuryl fluoride. </strong></span>Rabbits initially were exposed to a high concn of 600 ppm; however, convulsions were noted in two animals after nine exposures and the concn subsequently was reduced to 300 ppm. Vacuolation and/or malacia were observed in the cerebrum of all rabbits at the highest concn; one rabbit exposed to 100 ppm also had cerebral vacuolation. Rabbits at the highest concn, as well as one rabbit exposed to 100 ppm, had inflammation of the nasal tissues. Although repeated exposure of rabbits to 100 to 600 ppm <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>resulted in toxicity to the brain and respiratory system, no effects were detected in rabbits exposed to 30 ppm for 13 wk. <br
/>[Eisenbrandt DL, Nitschke KD; Fundam Appl Toxicol 12 (3): 540-57 (1989)]**PEER REVIEWED**</p><p>Groups of 35 to 36 pregnant Fischer 344 rats and 28 to 29 pregnant New Zealand White rabbits were exposed to 0, 25, 75, or 225 ppm of <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>vapor via inhalation for 6 hr/day on days 6 to 15 and 6 to 18 of gestation, respectively. Among rats, maternal water consumption was increased in the 225 ppm exposure group (p &lt; 0.05), but there were no indications of embryotoxicity, fetotoxicity, or teratogenicity in any of the exposed groups. Among rabbits, maternal weight loss during the exposure period (days 6 to 18) was observed in the 225 ppm group. Decr fetal body wt, considered secondary to maternal weight loss, were also observed at 225 ppm. However, no evidence of embryotoxicity or teratogenicity was observed among rabbits in any exposure group. For both species a low incidence of malformations were seen scattered among all exposure groups, with no indication of any treatment related effects. In preliminary studies, exposure of pregnant rats and rabbits to 30, 100, or 300 ppm <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>produced significantly decr maternal wt gain in both rats and rabbits exposed to 300 ppm. Increased absolute kidney wt (rats) and decr liver wt (rabbits) were also observed at this exposure level. No adverse effects were observed at either 30 or 100 ppm in either species. <br
/>[Hanley TR, et al; Fundam Appl Toxicol 13 (1): 79-86 (1989)]**PEER REVIEWED**</p><p>Animal exposures of 1000 ppm for 3 hr or of 15,000 ppm for 6 min were fatal to fewer than 5% of animals tested. /Species not specified/ <br
/>[Zenz, C. Occupational Medicine-Principles and Practical Applications. 2nd ed. St. Louis, MO: Mosby-Yearbook, Inc, 1988., p. 684]**PEER REVIEWED**</p><p>Both sexes of rats, guinea pigs, and rabbits and female rhesus monkeys tolerated air concentrations of 100 ppm (417 mg/cu m) without apparent adverse effect when exposed 7 hr a day, 5 days a wk, for 6 mo. Observations included survival, general appearance, behavior, and the appearance of internal organs of animals killed at the end of the experiment &#8230; Later it was reported that a concentration of 20 ppm produced detectable effects in rats, mice, and guinea pigs exposed 7 hr a day for 6 mo, but the injury present after 12 mo was reversible when exposure was discontinued. Some evidence of fluorosis was observed in the incisors of mice but not in those of rats or guinea pigs. &#8230; Although the long term effects of <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>are those of excess fluoride, it seems possible that some or all of the acute effects are those of the intact molecule. <br
/>[Hayes, W.J., Jr., E.R. Laws, Jr., (eds.). Handbook of Pesticide Toxicology. Volume 2. Classes of Pesticides. New York, NY: Academic Press, Inc., 1991., p. 564]**PEER REVIEWED**</p><p>A review of unpublished reports of animal experiments apparently &#8230; /indicated/ that dosages sufficient to produce illness from a single exposure produce respiratory irritation, CNS depression, and possible liver and kidney injury. <br
/>[Hayes, W.J., Jr., E.R. Laws, Jr., (eds.). Handbook of Pesticide Toxicology. Volume 2. Classes of Pesticides. New York, NY: Academic Press, Inc., 1991., p. 564]**PEER REVIEWED**</p><p>&#8230; PHYTOTOXIC BUT WITH LITTLE EFFECT ON THE GERMINATION OF WEED &amp; CROP SEEDS. <br
/>[Tomlin, C.D.S. (ed.). The Pesticide Manual - World Compendium. 10th ed. Surrey, UK: The British Crop Protection Council, 1994., p. 935]**PEER REVIEWED**</p><p>Pregnant Fischer 344 rats and New Zealand White rabbits were exposed to 0, 25, 75, or 225 ppm of <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>vapor via inhalation for 6 hr/day on days 6-15 and 6-18 of gestation, respectively. Among rats, maternal water consumption was increased in the 225 ppm exposure group, but there were no indications of embryotoxicity, fetotoxicity, or teratogenicity in any of the exposed groups. Among rabbits, maternal wt loss during the exposure period (days 6-18) was observed in the 225 ppm group. Decreased fetal body wt, considered secondary to maternal wt loss, were also observed at 225 ppm. However, no evidence of embryotoxicity or teratogenicity was observed among rabbits in any exposure group. Thus, inhalation exposure to <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>was not teratogenic in either rats or rabbits exposed to levels of up to 225 ppm, and fetotoxic effects (reduced body wt) were observed among fetal rabbits only at an exposure level that produced maternal wt loss. <br
/>[Hanley TR Jr et al; Fundam Appl Toxicol 13 (1): 79-86 (1989)]**PEER REVIEWED**</p><p>Male rats that inhaled 4000 ppm <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>survived about 2.5 hours; tonic convulsions were observed just prior to death. With exposure to concentrations up to 40,000 ppm, the time to death decreased in a concentration-dependent manner. Pulmonary edema, cyanosis, respiratory arrest, and convulsions preceded death at the higher concentrations. Because circulating fluoride was elevated in the animals that died, the authors considered that the toxicity of <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>was due, at least in part, to fluoride. <br
/>[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I, II, III. Cincinnati, OH: ACGIH, 1991., p. 1470]**PEER REVIEWED**</p><p><span
style="color: red;"><strong>Sulfuryl fluoride </strong></span>has been shown to induce renal and pulmonary injury on repeated exposure to high concentrations. Repeated inhalation of <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>by rats, guinea pigs, and mice at 20 ppm, 7 hours/day caused no significant effects in 6 months; however, after 12 months, there was slight injury which was reversed after exposure was terminated. Some evidence of fluorosis was observed in the incisors of mice; none was observed in the teeth of rats or guinea pigs. <br
/>[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I, II, III. Cincinnati, OH: ACGIH, 1991., p. 1470]**PEER REVIEWED**</p><p>Rats and rabbits were exposed at 100, 300, or 600 ppm <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>vapor 6 hours/day, 5 days/week for 2 weeks or to 30,100, or 300 ppm for 13 weeks. In the 2-week study, 9 of 10 rats died when exposed at 600 ppm; necropsy revealed extensive renal necrosis. The surviving rat had inflamed respiratory and nasal tissue, but only moderate kidney lesions. Minimal renal damage was seen in the rats exposed at 300 ppm. Rabbits exposed at 300 or 600 ppm demonstrated hyperactivity and developed convulsions, moderate inflammation of nasal tissues, and some inflammation of the trachea or bronchi. In the 13-week study, rats that inhaled 100 or 300 ppm had mottled incisors. Rats that inhaled 300 ppm developed minimal cerebral vacuolation, minimal signs of renal involvement, pulmonary histiocytosis, inflammation of nasal tissues, and slight, elevation in serum fluoride concentrations. Rabbits exposed at 100 ppm or 300 ppm had varying degrees of nasal tissue inflammation and significant elevation of serum fluoride concentrations. Serum fluoride was also elevated in the rabbits exposed at 30 ppm; however, exposure to this concentration did not induce toxicity in rats or rabbits. <br
/>[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I, II, III. Cincinnati, OH: ACGIH, 1991., p. 1470]**PEER REVIEWED**</p><p>When female rhesus monkeys inhaled 100 ppm (417 mg/cu m) <span
style="color: red;"><strong>sulfuryl fluoride, </strong></span>7 hours/day, 5 days/week for 6 months, their survival, general appearance, and behavior were reportedly unaffected. <br
/>[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I, II, III. Cincinnati, OH: ACGIH, 1991., p. 1470]**PEER REVIEWED**</p><p>Mice are more sensitive than rats to the acute effects of inhaled <span
style="color: red;"><strong>sulfuryl fluoride, </strong></span>whereas rabbits were considered somewhat less sensitive; tonic convulsions were recorded after exposure and aveolar hemorrhage/pulmonary congestion was seen in those that inhaled greater than or equal to 6000 ppm. <br
/>[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I, II, III. Cincinnati, OH: ACGIH, 1991., p. 1470]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Non-Human Toxicity Values:</strong></p><p>LD50 Rat oral 100 mg/kg <br
/>[Zenz, C. Occupational Medicine-Principles and Practical Applications. 2nd ed. St. Louis, MO: Mosby-Yearbook, Inc, 1988., p. 684]**PEER REVIEWED**</p><p>LD50 Guinea pig oral 100 mg/kg <br
/>[Zenz, C. Occupational Medicine-Principles and Practical Applications. 2nd ed. St. Louis, MO: Mosby-Yearbook, Inc, 1988., p. 684]**PEER REVIEWED**</p><p>NOEL Rat and Rabbit 30 ppm, 6 hr/day, 5 day/wk <br
/>[Tomlin, C.D.S. (ed.). The Pesticide Manual - World Compendium. 10th ed. Surrey, UK: The British Crop Protection Council, 1994., p. 935]**PEER REVIEWED**</p><p>LC50 Rat inhalation approx 1000 ppm/4 hr <br
/>[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I, II, III. Cincinnati, OH: ACGIH, 1991., p. 1470]**PEER REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Metabolism/Pharmacokinetics:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>Metabolism/Metabolites:</strong></p><p>In the absence of studies on mammals, it is necessary to refer to an excellent study on termites. First it was shown that termites fumigated with a nonlethal concentration of [35S]<span
style="color: red;"><strong>sulfuryl fluoride </strong></span>excreted inorganic sulfate, indicating that fluoride had been released. Then, using the labeled metabolic pool technique &#8230; separate studies of termites prefed on sodium [14C]acetate or on [32P]phosphate showed that fumigated termites exhibited aspectrum of metabolic changes characteristic of fluoride toxicity.<br
/>[Hayes, W.J., Jr., E.R. Laws, Jr., (eds.). Handbook of Pesticide Toxicology. Volume 2. Classes of Pesticides. New York, NY: Academic Press, Inc., 1991., p. 564]**PEER REVIEWED**</p><p>&#8230; It was shown that termites fumigated with a nonlethal concentration of (35)S <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>excreted inorganic sulfate, indicating that fluoride had been released. Then, using the labeled metabolic pool technique, separate studies of termites prefed sodium (14)C acetate or on (32)P phosphate showed that fumigated termites exhibited a spectrum of metabolic changes characteristic of fluoride toxicity. <br
/>[Hayes, W.J., Jr., E.R. Laws, Jr., (eds.). Handbook of Pesticide Toxicology. Volume 2. Classes of Pesticides. New York, NY: Academic Press, Inc., 1991., p. 564]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Absorption, Distribution &amp; Excretion:</strong></p><p>FLUORIDES ARE ABSORBED FROM GI TRACT, LUNG, &amp; SKIN. GI TRACT IS MAJOR SITE OF ABSORPTION. THE RELATIVELY SOL CMPD, SUCH AS SODIUM FLUORIDE, ARE ALMOST COMPLETELY ABSORBED. &#8230; FLUORIDE HAS BEEN DETECTED IN ALL ORGANS &amp; TISSUES, AND IT IS CONCENTRATED IN BONE, THYROID, AORTA, &amp; PERHAPS KIDNEY. FLUORIDE IS PRIMARILY DEPOSITED IN BONE &amp; TEETH, &amp; THE DEGREE OF SKELETAL STORAGE IS RELATED TO INTAKE AND AGE. &#8230; MAJOR ROUTE OF &#8230; EXCRETION IS VIA THE KIDNEYS; &#8230; /ALSO EXCRETED IN SMALL AMT/ IN SWEAT, MILK, AND INTESTINAL SECRETIONS. &#8230; ABOUT 90% OF FLUORIDE ION FILTERED BY GLOMERULUS IS REABSORBED BY RENAL TUBULES. /FLUORIDE/ <br
/>[Hardman, J.G., L.E. Limbird, P.B. Molinoff, R.W. Ruddon, A.G. Goodman (eds.). Goodman and Gilman's The Pharmacological Basis of Therapeutics. 9th ed. New York, NY: McGraw-Hill, 1996., p. 1538]**PEER REVIEWED**</p><p>Solutions of fluoride salts are rapidly and almost completely absorbed from the gastrointestinal tract, probably by simple diffusion &#8230; Less than 10% of the ingested fluoride is excreted in the feces, but the proportion varies with circumstances &#8230; The simultaneous presence of strongly fluoride-binding ions, especially calcium ions, will reduce the absorption of fluoride &#8230; In patients ingesting aluminum-containing antacids, fluoride absorption decr to about 40%, and the retention decr to nil. /Fluorides/ <br
/>[WHO; Environ Health Criteria 36: Fluorine and Fluorides p.37 (1984)]**PEER REVIEWED**</p><p>In the industrial environment, the respiratory tract is the major route of absorption of both gaseous and particulate fluoride. Hydrogen fluoride being highly soluble in water is rapidly taken up in the upper respiratory tract &#8230; Depending on their aerodynamic characteristics, fluoride-containing particles will be deposited in the nasopharynx, the tracheo-bronchial tree and the alveoli &#8230; Dermal absorption of fluoride has only been reported in the case of burns resulting from exposure to hydrofluoric acid &#8230; . /Fluorides/ <br
/>[WHO; Environ Health Criteria 36: Fluorine and Fluorides p.37 (1984)]**PEER REVIEWED**</p><p>About 75% of the blood fluoride is present in the plasma; the rest is mainly in or on the red blood cells &#8230; Fluoride in human serum exists in both ionic and nonionic forms. &#8230; For the general population under steady-state conditions of exposure, the concn of fluoride ions in plasma is directly related to the fluoride content of the drinking water. /Fluorides/ <br
/>[WHO; Environ Health Criteria 36: Fluorine and Fluorides p.38 (1984)]**PEER REVIEWED**</p><p>Fluoride ions are taken up rapidly by bone by replacing hydroxyl ions in bone apatite. /Fluorides/ <br
/>[WHO; Environ Health Criteria 36: Fluorine and Fluorides p.40 (1984)]**PEER REVIEWED**</p><p>In adult teeth, the fluoride content of the surface layer of enamel (thickness 10 um) is reported to be 900-1,000 mg/kg in areas with low fluoride levels in the water, about 1,500 mg/kg in fluoridated areas, and about 2,700 mg/kg in areas with fluoride concn in the drinking water of 3 mg/L &#8230; The average concn of fluoride in dentine is 2-3 times that in enamel and is affected by growth and mineralization. As with bone and enamel, dentin fluoride levels are higher in the surface (circumpulpal) regions than in the interior &#8230; . /Fluorides/ <br
/>[WHO; Environ Health Criteria 36: Fluorine and Fluorides p.41 (1984)]**PEER REVIEWED**</p><p>The principal route of fluoride excretion is via the urine. Some excretion takes place through sweat and feces, and fluoride also appears in saliva. Fluoride crosses the placenta; it rarely seems to be excreted in milk to any significant extent. /Fluorides/ <br
/>[WHO; Environ Health Criteria 36: Fluorine and Fluorides p.42 (1984)]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Biological Half-Life:</strong></p><p>&#8230; Bone retains about 60% of iv-injected fluoride and that the half-time for this uptake is only about 13 min; both blood and extracellular fluid levels therefore decr rapidly. After ingestion of sodium fluoride, plasma fluoride levels show a much slower change with a half-life of about 3 hr &#8230; . /Fluorides/ <br
/>[WHO; Environ Health Criteria 36: Fluorine and Fluorides p.38 (1984)]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Mechanism of Action:</strong></p><p>Fluoride is an inhibitor of several enzyme systems and diminishes tissue respiration and anaerobic glycolysis. &#8230; /it also/ binds Ca+2. It also inhibits erythrocyte glycolysis. /Fluoride/ <br
/>[Hardman, J.G., L.E. Limbird, P.B. Molinoff, R.W. Ruddon, A.G. Goodman (eds.). Goodman and Gilman's The Pharmacological Basis of Therapeutics. 9th ed. New York, NY: McGraw-Hill, 1996., p. 1538]**PEER REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Pharmacology:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>Drug Warnings:</strong></p><p>Food and Environmental Agents: Effect on Breast-Feeding: Reported Sign or Symptom in Infant or Effect on Lactation: Fluorides: None. /from Table 7/ <br
/>[Report of the American Academy of Pediatrics Committee on Drugs in Pediatrics 93 (1): 142 (1994)]**PEER REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Environmental Fate &amp; Exposure:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>Probable Routes of Human Exposure:</strong></p><p>Inhalation, eye and skin contact <br
/>[Sittig, M. Handbook of Toxic and Hazardous Chemicals and Carcinogens, 1985. 2nd ed. Park Ridge, NJ: Noyes Data Corporation, 1985., p. 820]**PEER REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Environmental Standards &amp; Regulations:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>FIFRA Requirements:</strong></p><p>As the federal pesticide law FIFRA directs, EPA is conducting a comprehensive review of older pesticides to consider their health and environmental effects and make decisions about their future use. Under this pesticide reregistration program, EPA examines health and safety data for pesticide active ingredients initially registered before November 1, 1984, and determines whether they are eligible for reregistration. In addition, all pesticides must meet the new safety standard of the Food Quality Protection Act of 1996. <span
style="color: red;"><strong>Sulfuryl fluoride </strong></span>is found on List A, which contains most food use pesticides and consists of the 194 chemical cases (or 350 individual active ingredients) for which EPA issued registration standards prior to FIFRA, as amended in 1988. Case No: 0176; Pesticide type: antimicrobial; Registration Standard Date: 06/30/85; Case Status: RED Approved 09/93; OPP has made a decision that some/all uses of the pesticide are eligible for reregistration, as reflected in a Reregistration Eligibility Decision (RED) document.; Active ingredient (AI): <span
style="color: red;"><strong>Sulfuryl fluoride; </strong></span>Data Call-in (DCI) Date(s): 07/20/90, 11/10/92, 09/30/93; AI Status: OPP has completed a Reregistration Eligibility Decision (RED) document for the case/AI. <br
/>[USEPA/OPP; Status of Pesticides in Registration, Reregistration and Special Review p.150 (Spring, 1998) EPA 738-R-98-002]**QC REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Chemical/Physical Properties:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>Molecular Formula:</strong></p><p>F2-O2-S <br
/>[Budavari, S. (ed.). The Merck Index - Encyclopedia of Chemicals, Drugs and Biologicals. Rahway, NJ: Merck and Co., Inc., 1989., p. 1419]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Molecular Weight:</strong></p><p>102.06 <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Color/Form:</strong></p><p>COLORLESS GAS <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p>Colorless compressed gas <br
/>[Farm Chemicals Handbook 1997. Willoughby, OH: Meister Publishing Co., 1997., p. C-389]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Odor:</strong></p><p>ODORLESS <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p>Odorless. <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 94-116. Washington, D.C.: U.S. Government Printing Office, June 1994., p. 292]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Boiling Point:</strong></p><p>-55.38 DEG C <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Melting Point:</strong></p><p>-135.82 DEG C <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Corrosivity:</strong></p><p>NON-CORROSIVE <br
/>[Worthing, C.R. and S.B. Walker (eds.). The Pesticide Manual - A World Compendium. 8th ed. Thornton Heath, UK: The British Crop Protection Council, 1987., p. 758]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Critical Temperature &amp; Pressure:</strong></p><p>CRITICAL TEMP: 96 + OR &#8211; 20 DEG C <br
/>[Worthing, C. R. (ed.). Pesticide Manual. 6th ed. Worcestershire, England: British Crop Protection Council, l979., p. 488]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Density/Specific Gravity:</strong></p><p>3.72 G/L (GAS), 1.7 G/L (LIQ) <br
/>[Lide, D.R. (ed.). CRC Handbook of Chemistry and Physics. 73rd ed. Boca Raton, FL: CRC Press Inc., 1992-1993., p. 4-104]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Solubilities:</strong></p><p>4-5 ML GAS/100 ML WATER; 24-27 ML GAS/100 ML ALC; 136-138 ML GAS/100 ML CARBON TETRACHLORIDE; 210-220 ML GAS/100 ML TOLUENE <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p>SLIGHTLY SOL IN ALKALIS <br
/>[American Conference of Governmental Industrial Hygienists. Documentation of the Threshold Limit Values and Biological Exposure Indices. 5th ed. Cincinnati, OH: American Conference of Governmental Industrial Hygienists, 1986., p. 546]**PEER REVIEWED**</p><p>MISCIBLE WITH METHYL BROMIDE; SPARINGLY SOL IN MOST ORG SOLVENTS <br
/>[Worthing, C. R. (ed.). Pesticide Manual. 6th ed. Worcestershire, England: British Crop Protection Council, l979., p. 488]**PEER REVIEWED**</p><p>In water 750 mg/kg @ 25 deg C, 1 atm; in ethanol 0.24 to 0.27 l/l; in toluene 2.1 to 2.2 l/l; in carbon tetrachloride 1.36 to I.38 l/l <br
/>[Tomlin, C.D.S. (ed.). The Pesticide Manual - World Compendium. 10th ed. Surrey, UK: The British Crop Protection Council, 1994., p. 935]**PEER REVIEWED**</p><p>Slightly soluble in cold water and most organic solvents. <br
/>[Lewis, R.J., Sr (Ed.). Hawley's Condensed Chemical Dictionary. 12th ed. New York, NY: Van Nostrand Rheinhold Co., 1993, p. 1105]**PEER REVIEWED**</p><p>Water solubility = 750 ppm at 77 deg F (25 deg C), 1 atm <br
/>[Farm Chemicals Handbook 1997. Willoughby, OH: Meister Publishing Co., 1997., p. C-389]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Vapor Density:</strong></p><p>3.5 (Air= 1) <br
/>[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) Publication No. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981., p. ]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Vapor Pressure:</strong></p><p>1.7X10+6 Pa at 21.1 deg C (12.750 mm Hg at 21.1 deg C) <br
/>[Tomlin, C.D.S. (ed.). The Pesticide Manual - World Compendium. 10th ed. Surrey, UK: The British Crop Protection Council, 1994., p. 935]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Other Chemical/Physical Properties:</strong></p><p>NOT HYDROLYZED BY WATER; HYDROLYZED BY SODIUM HYDROXIDE SOLN; NOT VERY REACTIVE <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p>Stable to light; stable up to about 500 deg C when dry; rapidly hydrolyzed by aqueous alkali, but not by water. <br
/>[Tomlin, C.D.S. (ed.). The Pesticide Manual - World Compendium. 10th ed. Surrey, UK: The British Crop Protection Council, 1994., p. 935]**PEER REVIEWED**</p><p>Freezing point = -136.7 deg C <br
/>[Lewis, R.J., Sr (Ed.). Hawley's Condensed Chemical Dictionary. 12th ed. New York, NY: Van Nostrand Rheinhold Co., 1993, p. 1105]**PEER REVIEWED**</p><p>Density = 4.478 g/l <br
/>[Lide, D.R. (ed.). CRC Handbook of Chemistry and Physics. 76th ed. Boca Raton, FL: CRC Press Inc., 1995-1996., p. 4-88]**PEER REVIEWED**</p><p>Vapor pressure = 9150 mm Hg at 50 deg F (10 deg C) <br
/>[Farm Chemicals Handbook 1997. Willoughby, OH: Meister Publishing Co., 1997., p. C-389]**PEER REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Chemical Safety &amp; Handling:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>DOT Emergency Guidelines:</strong></p><p>Health: TOXIC; may be fatal if inhaled or absorbed through skin. Vapors may be irritating. Contact with gas or liquefied gas may cause burns, severe injury and/or frostbite. Fire will produce irritating, corrosive and/or toxic gases. Runoff from fire control may cause pollution. <br
/>[U.S. Department of Transportation. 2000 Emergency Response Guidebook. RSPA P 5800.8 Edition. Washington, D.C: U.S. Government Printing Office, 2000,p. G-123]**QC REVIEWED**</p><p>Fire or explosion: Some may burn, but none ignite readily. Vapors from liquefied gas are initially heavier than air and spread along ground. Containers may explode when heated. Ruptured cylinders may rocket. <br
/>[U.S. Department of Transportation. 2000 Emergency Response Guidebook. RSPA P 5800.8 Edition. Washington, D.C: U.S. Government Printing Office, 2000,p. G-123]**QC REVIEWED**</p><p>Public safety: CALL Emergency Response Telephone Number. &#8230; Isolate spill or leak area immediately for at least 100 to 200 meters (330 to 660 feet) in all directions. Keep unauthorized personnel away. Stay upwind. Many gases are heavier than air and will spread along ground and collect in low or confined areas (sewers, basements, tanks). Keep out of low areas. Ventilate closed spaces before entering. <br
/>[U.S. Department of Transportation. 2000 Emergency Response Guidebook. RSPA P 5800.8 Edition. Washington, D.C: U.S. Government Printing Office, 2000,p. G-123]**QC REVIEWED**</p><p>Protective clothing: Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing which is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters&#8217; protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations. <br
/>[U.S. Department of Transportation. 2000 Emergency Response Guidebook. RSPA P 5800.8 Edition. Washington, D.C: U.S. Government Printing Office, 2000,p. G-123]**QC REVIEWED**</p><p>Evacuation: &#8230; Fire: If tank, rail car or tank truck is involved in a fire, ISOLATE for 800 meters (1/2 mile) in all directions; also, consider initial evacuation for 800 meters (1/2 mile) in all directions. <br
/>[U.S. Department of Transportation. 2000 Emergency Response Guidebook. RSPA P 5800.8 Edition. Washington, D.C: U.S. Government Printing Office, 2000,p. G-123]**QC REVIEWED**</p><p>Fire: Small Fires: Dry chemical or CO2. Large Fires: Water spray, fog or regular foam. Do not get water inside containers. Move containers from fire area if you can do it without risk. Damaged cylinders should be handled only by specialists. Fire involving tanks: Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Cool containers with flooding quantities of water until well after fire is out. Do not direct water at source of leak or safety devices; icing may occur. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. Always stay away from tanks engulfed in fire. <br
/>[U.S. Department of Transportation. 2000 Emergency Response Guidebook. RSPA P 5800.8 Edition. Washington, D.C: U.S. Government Printing Office, 2000,p. G-123]**QC REVIEWED**</p><p>Spill or leak: Fully encapsulating, vapor protective clothing should be worn for spills and leaks with no fire. Do not touch or walk through spilled material. Stop leak if you can do it without risk. If possible, turn leaking containers so that gas escapes rather than liquid. Prevent entry into waterways, sewers, basements or confined areas. Use water spray to reduce vapors or divert vapor cloud drift. Avoid allowing water runoff to contact spilled material. Do not direct water at spill or source of leak. Isolate area until gas has dispersed. <br
/>[U.S. Department of Transportation. 2000 Emergency Response Guidebook. RSPA P 5800.8 Edition. Washington, D.C: U.S. Government Printing Office, 2000,p. G-123]**QC REVIEWED**</p><p>First aid: Move victim to fresh air. Call 911 or emergency medical service. Apply artificial respiration if victim is not breathing. Do not use mouth-to-mouth method if victim ingested or inhaled the substance; induce artificial respiration with the aid of a pocket mask equipped with a one-way valve or other proper respiratory medical device. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with liquefied gas, thaw frosted parts with lukewarm water. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. Keep victim warm and quiet. Keep victim under observation. Effects of contact or inhalation may be delayed. Ensure that medical personnel are aware of the material(s) involved, and take precautions to protect themselves. <br
/>[U.S. Department of Transportation. 2000 Emergency Response Guidebook. RSPA P 5800.8 Edition. Washington, D.C: U.S. Government Printing Office, 2000,p. G-123]**QC REVIEWED**</p><p>Initial Isolation and Protective Action Distances: Small Spills (from a small package or small leak from a large package): First, ISOLATE in all Directions 30 meters (100 feet); then, PROTECT persons Downwind during DAY 0.2 kilometers (0.1 miles) and NIGHT 0.3 kilometers (0.2 miles). LARGE SPILLS (from a large package or from many small packages): First, ISOLATE in all Directions 95 meters (300 feet); then, PROTECT persons Downwind during DAY 0.8 kilometers (0.5 miles) and NIGHT 2.3 kilometers (1.4 miles). <br
/>[U.S. Department of Transportation. 2000 Emergency Response Guidebook. RSPA P 5800.8 Edition. Washington, D.C: U.S. Government Printing Office, 2000,p. TABLE]**QC REVIEWED**</p><p>&nbsp;</p><p><strong>Skin, Eye and Respiratory Irritations:</strong></p><p>HIGHLY IRRITATING TO RESPIRATORY TRACT. <br
/>[Budavari, S. (ed.). The Merck Index - Encyclopedia of Chemicals, Drugs and Biologicals. Rahway, NJ: Merck and Co., Inc., 1989., p. 1419]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Fire Fighting Procedures:</strong></p><p>If material involved in fire: extinguish fire using agent suitable for type of surrounding fire. (Material itself does not burn or burns with difficulty.) Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible. <br
/>[Association of American Railroads. Emergency Handling of Hazardous Materials in Surface Transportation. Washington, DC: Association of American Railroads, Bureau of Explosives, 1994., p. 1024]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Explosive Limits &amp; Potential:</strong></p><p>Non-combustible <br
/>[Lewis, R.J., Sr (Ed.). Hawley's Condensed Chemical Dictionary. 12th ed. New York, NY: Van Nostrand Rheinhold Co., 1993, p. 1105]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Hazardous Reactivities &amp; Incompatibilities:</strong></p><p>CAN REACT WITH WATER, STEAM. <br
/>[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996., p. 3050]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Hazardous Decomposition:</strong></p><p>WHEN HEATED TO DECOMPOSITION IT EMITS VERY TOXIC FUMES OF &#8230; /HYDROGEN FLUORIDE AND SULFUR OXIDES/. <br
/>[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996., p. 3051]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Immediately Dangerous to Life or Health:</strong></p><p>200 ppm <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 292]**QC REVIEWED**</p><p>&nbsp;</p><p><strong>Protective Equipment &amp; Clothing:</strong></p><p>A self-contained breathing apparatus or full face gas mask with acid gas/organicvapor canister, approved by NIOSH &#8230; . <br
/>[Farm Chemicals Handbook 1984. Willoughby, Ohio: Meister Publishing Co., 1984., p. C-241]**PEER REVIEWED**</p><p>Recommendations for respirator selection. Max concn for use: 50 ppm: Respirator Classes: Any supplied-air respirator. May require eye protection. <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 293]**QC REVIEWED**</p><p>Recommendations for respirator selection. Max concn for use: 125 ppm Respirator Class: Any supplied-air respirator operated in a continuous flow mode. May require eye protection. <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 293]**QC REVIEWED**</p><p>Recommendations for respirator selection. Max concn for use: 200 ppm Respirator Classes: Any self-contained breathing apparatus with a full facepiece. Any supplied-air respirator with a full facepiece. <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 293]**QC REVIEWED**</p><p>Recommendations for respirator selection. Condition: Emergency or planned entry into unknown concn or IDLH conditions: Respirator Classes: Any self-contained breathing apparatus that has a full facepiece and is operated in a pressure-demand or other positive pressure mode. Any supplied-air respirator with a full facepiece and operated in pressure-demand or other positive pressure mode in combination with an auxiliary self-contained breathing apparatus operated in pressure-demand or other positive pressure mode. <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 293]**QC REVIEWED**</p><p>Recommendations for respirator selection. Condition: Escape from suddenly occurring respiratory hazards: Respirator Classes: Any air purifying, full facepiece respirator (gas mask) with a chin-style, front- or back-mounted canister providing protection against the compound of concern. Any appropriate escape type, self contained breathing apparatus. <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 293]**QC REVIEWED**</p><p>Wear appropriate personal protective clothing to prevent the skin from becoming frozen from contact with the liquid or from contact with vessels containing the liquid. <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 293]**QC REVIEWED**</p><p>SRP: Contaminated protective clothing should be segregated in such a manner so that there is no direct personal contact by personnel who handle, dispose, or clean the clothing. Quality assurance to ascertain the completeness of the cleaning procedures should be implemented before the decontaminated protective clothing is returned for reuse by the workers. Contaminated clothing should not be taken home at end of shift, but should remain at employee&#8217;s place of work for cleaning. <br
/>**PEER REVIEWED**</p><p>Wear appropriate eye protection to prevent eye contact with the liquid that could result in burns or tissue damage from frostbite. <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 293]**QC REVIEWED**</p><p>Quick drench facilities and/or eyewash fountains should be provided within the immediate work area for emergency use where there is any possibility of exposure to liquids that are extremely cold or rapidly evaporating. <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 293]**QC REVIEWED**</p><p>&nbsp;</p><p><strong>Preventive Measures:</strong></p><p>SRP: The scientific literature for the use of contact lenses in industry is conflicting. The benefit or detrimental effects of wearing contact lenses depend not only upon the substance, but also on factors including the form of the substance, characteristics and duration of the exposure, the uses of other eye protection equipment, and the hygiene of the lenses. However, there may be individual substances whose irritating or corrosive properties are such that the wearing of contact lenses would be harmful to the eye. In those specific cases, contact lenses should not be worn. In any event, the usual eye protection equipment should be worn even when contact lenses are in place. <br
/>**PEER REVIEWED**</p><p>If material not involved in fire: Attempt to stop leak if without undue personnel hazard. <br
/>[Association of American Railroads. Emergency Handling of Hazardous Materials in Surface Transportation. Washington, DC: Association of American Railroads, Bureau of Explosives, 1994., p. 1024]**PEER REVIEWED**</p><p>Personnel protection: Avoid breathing vapors. Keep upwind. &#8230; Do not handle broken packages unless wearing appropriate personal protective equipment. <br
/>[Association of American Railroads. Emergency Handling of Hazardous Materials in Surface Transportation. Washington, DC: Association of American Railroads, Bureau of Explosives, 1994., p. 1024]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Stability/Shelf Life:</strong></p><p>STABLE TO 400 DEG C <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p>Stable to light. Stable up to approx 500 deg C when dry. Rapidly hydrolyzed by aqueous alkali, but not by water. <br
/>[Tomlin, C.D.S. (ed.). The Pesticide Manual - World Compendium. 10th ed. Surrey, UK: The British Crop Protection Council, 1994., p. 935]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Shipment Methods and Regulations:</strong></p><p>No person may /transport,/ offer or accept a hazardous material for transportation in commerce unless that person is registered in conformance &#8230; and the hazardous material is properly classed, described, packaged, marked, labeled, and in condition for shipment as required or authorized by &#8230; /the hazardous materials regulations (49 CFR 171-177)./ <br
/>[49 CFR 171.2 (7/1/96)]**PEER REVIEWED**</p><p>The International Air Transport Association (IATA) Dangerous Goods Regulations are published by the IATA Dangerous Goods Board pursuant to IATA Resolutions 618 and 619 and constitute a manual of industry carrier regulations to be followed by all IATA Member airlines when transporting hazardous materials. <br
/>[IATA. Dangerous Goods Regulations. 38th ed. Montreal, Canada and Geneva, Switzerland: International Air Transport Association, Dangerous Goods Board, January, 1997., p. 217]**PEER REVIEWED**</p><p>The International Maritime Dangerous Goods Code lays down basic principles for transporting hazardous chemicals. Detailed recommendations for individual substances and a number of recommendations for good practice are included in the classes dealing with such substances. A general index of technical names has also been compiled. This index should always be consulted when attempting to locate the appropriate procedures to be used when shipping any substance or article. <br
/>[IMDG; International Maritime Dangerous Goods Code; International Maritime Organization p.2114-2 (1988)]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Storage Conditions:</strong></p><p>MAY BE STORED IN COMPRESSED FORM IN STEEL CYLINDERS OR IN GASOMETER OVER SULFURIC ACID. <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p>Store cylinders upright, away from heat in a secured, well ventilated area away from dwellings and work areas. Do not contaminate or store near food, feed, or drugs. When not in use, all full and partially used or empty cylinders must have the valve closed and the valve cover hood securely in place. <br
/>[Farm Chemicals Handbook 1984. Willoughby, Ohio: Meister Publishing Co., 1984., p. C-241]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Disposal Methods:</strong></p><p>SRP: At the time of review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices. <br
/>**PEER REVIEWED**</p><p>The following disposal method has been suggested &#8230; allow gas to flow into a mixed solution of caustic soda and slaked lime. <br
/>[Sittig, M. (ed.) Pesticide Manufacturing and Toxic Materials Control Encyclopedia. Park Ridge, NJ: Noyes Data Corporation. 1980., p. 693]**PEER REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Occupational Exposure Standards:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><a
name="occ1"></a> <strong>OSHA Standards:</strong></p><p>Permissible Exposure Limit: Table Z-1 8-hr Time Weighted Avg: 5 ppm (20 mg/cu m). <br
/>[29 CFR 1910.1000 (7/1/98)]**QC REVIEWED**</p><p>Vacated 1989 OSHA PEL TWA 5 ppm (20 mg/cu m); STEL 10 ppm (40 mg/cu m) is still enforced in some states. <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 372]**QC REVIEWED**</p><p>&nbsp;</p><p><strong>Threshold Limit Values:</strong></p><p>8 hr Time Weighted Avg (TWA): 5 ppm; 15 min Short Term Exposure Limit (STEL): 10 ppm. <br
/>[ American Conference of Governmental Industrial Hygienists TLVs and BEIs. Threshold Limit Values for Chemical Substances and Physical Agents and Biological Exposure Indices. Cincinnati, OH, 2005, p. 52]**QC REVIEWED**</p><p>&nbsp;</p><p><strong>NIOSH Recommendations:</strong></p><p>Recommended Exposure Limit: 10 Hr Time-Weighted Avg: 5 ppm (20 mg/cu m). <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 292]**QC REVIEWED**</p><p>Recommended Exposure Limit: 15 Min Short-Term Exposure Limit: 10 ppm (40 mg/cu m). <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 292]**QC REVIEWED**</p><p>&nbsp;</p><p><strong>Immediately Dangerous to Life or Health:</strong></p><p>200 ppm <br
/>[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997., p. 292]**QC REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Manufacturing/Use Information:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>Major Uses:</strong></p><p>INSECTICIDE &amp; FUMIGANT <br
/>[American Conference of Governmental Industrial Hygienists. Documentation of the Threshold Limit Values and Biological Exposure Indices. 5th ed. Cincinnati, OH: American Conference of Governmental Industrial Hygienists, 1986., p. 546]**PEER REVIEWED**</p><p><span
style="color: red;"><strong>SULFURYL FLUORIDE </strong></span>IS AN INSECTICIDE USED FOR FUMIGATING STRUCTURES, VEHICLES &amp; WOOD PRODUCTS TO CONTROL DRYWOOD TERMITES &amp; WOOD-INFESTING BEETLES&#8230; . <br
/>[Worthing, C.R. and S.B. Walker (eds.). The Pesticide Manual - A World Compendium. 8th ed. Thornton Heath, UK: The British Crop Protection Council, 1987., p. 758]**PEER REVIEWED**</p><p>&#8230; Used in organic synthesis of drugs and dyes. <br
/>[Sittig, M. Handbook of Toxic and Hazardous Chemicals and Carcinogens, 1985. 2nd ed. Park Ridge, NJ: Noyes Data Corporation, 1985., p. 820]**PEER REVIEWED**</p><p>Used as a fumigant for control Blattodea, Coleoptra, Isoptera, Lepidoptera, and rodents <br
/>[Tomlin, C.D.S. (ed.). The Pesticide Manual - World Compendium. 10th ed. Surrey, UK: The British Crop Protection Council, 1994., p. 935]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Manufacturers:</strong></p><p>DowElanco Inc, Hq, 9330 Zionsville Rd, Indianapolis, IN 46268, (317) 337-3000; Production site: Pittsburg, CA 94565 <br
/>[SRI. 1997 Directory of Chemical Producers -United States of America. Menlo Park, CA: SRI International 1997., p. 798]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Methods of Manufacturing:</strong></p><p>MADE BY THERMAL DECOMP OF BARIUM DI(FLUOROSULFATE) &#8230; . <br
/>[Worthing, C. R. (ed.). Pesticide Manual. 6th ed. Worcestershire, England: British Crop Protection Council, l979., p. 488]**PEER REVIEWED**</p><p>Prepared by heating barium difluorosulfite; alternate preparation from silver fluoride and sulfur dioxide. <br
/>[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996., p. 1536]**PEER REVIEWED**</p><p><span
style="color: red;"><strong>Sulfuryl fluoride </strong></span>may be made by: burning fluorine in sulfur dioxide; heating barium fluorosulfonate. <br
/>[Sittig, M. (ed.) Pesticide Manufacturing and Toxic Materials Control Encyclopedia. Park Ridge, NJ: Noyes Data Corporation. 1980., p. 693]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>General Manufacturing Information:</strong></p><p>UNDER CONDITIONS OF USAGE AS A GRAIN FUMIGANT, <span
style="color: red;"><strong>SULFURYL FLUORIDE </strong></span>REACTED WITH PROTEIN AND RELEASED INORGANIC FLUORIDE. SOME SULFATE WAS ALSO FOUND. <br
/>[Menzie, C.M. Metabolism of Pesticides. U.S. Department of the Interior, Bureau of Sport Fisheries and Wildlife, Publication 127. Washington, DC: U.S. Government Printing Office, 1969., p. 290]**PEER REVIEWED**</p><p>Introduced in 1957 by Dow Chemical Co under trade mark &#8216;<span
style="color: red;"><strong>vikane</strong></span>&#8216;. <br
/>[Worthing, C. R. (ed.). Pesticide Manual. 6th ed. Worcestershire, England: British Crop Protection Council, l979., p. 488]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Formulations/Preparations:</strong></p><p>IT IS USED AS THE 99% M/M /PROPORTION BY MASS/ TECHNICAL PRODUCT. <br
/>[Worthing, C.R. and S.B. Walker (eds.). The Pesticide Manual - A World Compendium. 8th ed. Thornton Heath, UK: The British Crop Protection Council, 1987., p. 758]**PEER REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Laboratory Methods:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>Clinical Laboratory Methods:</strong></p><p>NIOSH Method 8308. Analyte: Fluoride ion. Specimen: Urine, pre- and post-shift. Procedure: Ion selective electrode. For fluoride ion this method has an estimated detection limit of 0.1 mg/l urine sample. The precision/RSD is 0.04 and the recovery is 0.95. The working range is 1 to 100 mg/l urine for a 50 ml sample. Applicability: Any fluorine containing substances that can be metabolized to fluoride can be monitored using this procedure. Interferences: Hydroxide, the only positive interference, is eliminated by use of the buffer. /Fluoride ion/ <br
/>[U.S. Department of Health and Human Services, Public Health Service. Centers for Disease Control, National Institute for Occupational Safety and Health. NIOSH Manual of Analytical Methods, 3rd ed. Volumes 1 and 2 with 1985 supplement, and revisions. Washington, DC: U.S. Government Printing Office, February 1984., p. 8308-1]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Analytic Laboratory Methods:</strong></p><p>A method is described for the collection and determination of <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>in air. The <span
style="color: red;"><strong>sulfuryl fluoride </strong></span>is extracted with diluted sodium hydroxide, evaporated (an aliquot) to dryness, and determined by ion chromatography. An average recovery of 95.8% with standard deviation of 11% was obtained for a concn range of 1.0 to 10 ppm for 4 hr sampling periods. <br
/>[Bouyoucos SA et al; Am Ind Hyg Assoc J 44 (1): 57-61 (1983)]**PEER REVIEWED**</p><p>NIOSH Method 117. Analyte: Total fluoride. Matrix: Air. Procedure: Ion specific electrode. Method Evaluation: Method was validated over the range of 0.05 to 475 mg/cu m using a 40 liter sample. Method detection limit: Not determined. Precision (Coefficient of Variation): 0.065. Applicability: Under the conditions of sample size (40 liter) the useful range is 0.05 to 0.5 mg/cu m. Interferences: Hydroxide ion and monofluorophosphate ion. /Total fluoride/ <br
/>[U.S. Department of Health, Education Welfare, Public Health Service. Center for Disease Control, National Institute for Occupational Safety Health. NIOSH Manual of Analytical Methods. 2nd ed. Volumes 1-7. Washington, DC: U.S. Government Printing Office, 1977-present., p. V1 117-1]**PEER REVIEWED**</p><p>NIOSH Method S245. Analyte: <span
style="color: red;"><strong>Sulfuryl fluoride. </strong></span>Matrix: Air. Procedure: Gas chromatography with flame photometric detection. Method Evaluation: Method was validated over the range of 2.54 to 10.29 ppm using a 3 liter sample. Method detection limit: 0.1 ppm. Precision (CVT): 0.025. Applicability: Under the conditions of sample size (3 ppm) the useful range was 1X10+4. Interferences: No specific interferences. <br
/>[U.S. Department of Health, Education Welfare, Public Health Service. Center for Disease Control, National Institute for Occupational Safety Health. NIOSH Manual of Analytical Methods. 2nd ed. Volumes 1-7. Washington, DC: U.S. Government Printing Office, 1977-present., p. V6 S245-1]**PEER REVIEWED**</p><p>Analysis by GLC, IR spectrometry or by an instrument that pyrolyses <span
style="color: red;"><strong>sulfuryl fluoride (</strong></span>measuring the resultant sulfur dioxide); atmospheres analyzed by trapping in aqueous alkali and titration of the fluorosulfate produced; or a thermal conductivity meter (SG Heuser; Anal Chem 35: 1476 (1963)). <br
/>[Tomlin, C.D.S. (ed.). The Pesticide Manual - World Compendium. 10th ed. Surrey, UK: The British Crop Protection Council, 1994., p. 935]**PEER REVIEWED**</p><p>NIOSH Method 6012: <span
style="color: red;"><strong>Sulfuryl Fluoride </strong></span>by Ion Chromatography; Determination of <span
style="color: red;"><strong>Sulfuryl Fluoride </strong></span>by Ion Chromatography with Conductivity Detection; Ion chromatography/conductivity detection, workplace air, detection limit of 0.70 mg/cu-m. <br
/>[USEPA; EMMI. Environmental Monitoring Methods Index. Version 2.0. NTIS PB-95-502415 (1995)]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Sampling Procedures:</strong></p><p>Worker breathing-zone or area samples are collected by pumping air through a glass tube containing 1 g of activated charcoal. <br
/>[Bouyoucos SA et al; Am Ind Hyg Assoc J 44 (1): 57-61 (1983)]**PEER REVIEWED**</p><p>NIOSH Method S245. Analyte: <span
style="color: red;"><strong>Sulfuryl fluoride. </strong></span>Matrix: Air. Procedure: Collection in gas sampling bag. Flow Rate: 0.05 l/min or less. Sample Size: 3 liters. <br
/>[U.S. Department of Health, Education Welfare, Public Health Service. Center for Disease Control, National Institute for Occupational Safety Health. NIOSH Manual of Analytical Methods. 2nd ed. Volumes 1-7. Washington, DC: U.S. Government Printing Office, 1977-present., p. V6 S245-1]**PEER REVIEWED**</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Special References:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><span
style="font-size: 8pt;"><strong>Synonyms and Identifiers:</strong></span></p><p>&nbsp;</p><p>&nbsp;</p><p><strong>Synonyms:</strong></p><p>FLUORO DE SULFURILO (ITALIAN) <br
/>**PEER REVIEWED**</p><p>FLUORURE DE SULFURYLE (FRENCH) <br
/>**PEER REVIEWED**</p><p><span
style="color: red;"><strong>SULFONYL FLUORIDE </strong></span><br
/>**PEER REVIEWED**</p><p>SULFUR DIFLUORIDE DIOXIDE <br
/>**PEER REVIEWED**</p><p><span
style="color: red;"><strong>SULFURIC OXYFLUORIDE </strong></span><br
/>**PEER REVIEWED**</p><p><span
style="color: red;"><strong>SULPHURYL DIFLUORIDE </strong></span><br
/>**PEER REVIEWED**</p><p><span
style="color: red;"><strong>VIKANE</strong></span> <br
/>**PEER REVIEWED**</p><p><span
style="color: red;"><strong>VIKANE</strong></span> FUMIGANT <br
/>**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Formulations/Preparations:</strong></p><p>IT IS USED AS THE 99% M/M /PROPORTION BY MASS/ TECHNICAL PRODUCT. <br
/>[Worthing, C.R. and S.B. Walker (eds.). The Pesticide Manual - A World Compendium. 8th ed. Thornton Heath, UK: The British Crop Protection Council, 1987., p. 758]**PEER REVIEWED**</p><p>&nbsp;</p><p><strong>Shipping Name/ Number DOT/UN/NA/IMO:</strong></p><p>UN 2191; <span
style="color: red;"><strong>SULFURYL FLUORIDE</strong></span></p><p>IMO 2.3; <span
style="color: red;"><strong>SULFURYL FLUORIDE</strong></span></p> ]]></content:encoded> <wfw:commentRss>http://www.vikanemonitor.com/sulfuryl-fluoride-toxicology/feed/</wfw:commentRss> <slash:comments>0</slash:comments> </item> <item><title>Sulfuryl fluoride monitor&#8211;Controls, accessories, operation, and maintenance</title><link>http://www.vikanemonitor.com/sulfuryl-fluoride-monitor-controls-accessories-operation-and-maintenance/</link> <comments>http://www.vikanemonitor.com/sulfuryl-fluoride-monitor-controls-accessories-operation-and-maintenance/#comments</comments> <pubDate>Sun, 15 Jan 2012 20:49:20 +0000</pubDate> <dc:creator>vikane.admin</dc:creator> <category><![CDATA[Calibration, Maintenance, and Performance]]></category><guid
isPermaLink="false">http://www.vikanemonitor.com/index2.php/?p=91</guid> <description><![CDATA[<p>SO2F2 Monitor—Controls, accessories, operation, and maintenance, as presented to the Fumigator Group of Southern California in May of 2009 (1.3 MB) Click on above link to download pdf version of the training presentation</p> ]]></description> <content:encoded><![CDATA[<div><span
style="font-size: large;"><a
href="http://www.vikanemonitor.com/images/sulfuryl_fluoride_monitor_controls_accessories_operation_maintenance.pdf">SO<sub>2</sub>F<sub>2</sub> Monitor—Controls, accessories, operation, and maintenance</a>, as presented to the Fumigator Group of Southern California in May of 2009 <a
href="http://www.adobe.com/products/acrobat/readstep2.html"><img
src="http://www.adobe.com/products/acrobat/readstep2.html" alt="Get the Acrobat Reader" width="88" height="83" align="right" border="0" hspace="25" vspace="25" /></a> (1.3 MB)</span></div><div></div><div><span
id="more-91"></span>Click on above link to download pdf version of the training presentation</div> ]]></content:encoded> <wfw:commentRss>http://www.vikanemonitor.com/sulfuryl-fluoride-monitor-controls-accessories-operation-and-maintenance/feed/</wfw:commentRss> <slash:comments>0</slash:comments> </item> <item><title>Reading 1 ppm on legacy Interscan sulfuryl fluoride monitors [Model GF-1900]</title><link>http://www.vikanemonitor.com/reading-1-ppm-on-legacy-interscan-sulfuryl-fluoride-monitors-model-gf-1900/</link> <comments>http://www.vikanemonitor.com/reading-1-ppm-on-legacy-interscan-sulfuryl-fluoride-monitors-model-gf-1900/#comments</comments> <pubDate>Sun, 15 Jan 2012 20:47:55 +0000</pubDate> <dc:creator>vikane.admin</dc:creator> <category><![CDATA[Best Practices]]></category><guid
isPermaLink="false">http://www.vikanemonitor.com/index2.php/?p=89</guid> <description><![CDATA[<p>1.0 Background 1.1 Historical In the mid-1980’s, Interscan developed an instrument to be used in the clearance of structures treated with Vikane® gas fumigant. At the time, the reentry level was set at 10 ppm (parts-per-million). The measuring range of the instrument was 0-50 ppm,&#8230; <a
class="more-link" href="http://www.vikanemonitor.com/reading-1-ppm-on-legacy-interscan-sulfuryl-fluoride-monitors-model-gf-1900/">Continue reading <span
class="meta-nav">&#8594;</span></a></p> ]]></description> <content:encoded><![CDATA[<div
style="margin: 0in 0in 0pt;"><div
style="margin: 0in 0in 0pt; text-align: center;"><strong><span
style="font-size: 18pt;"><img
class="alignright" style="margin: 12px; border: 0pt none;" src="http://www.vikanemonitor.com/images/best_practices.jpg" alt="" width="163" height="120" align="right" border="0" hspace="12" vspace="12" /></span></strong></div><p><strong><span
style="font-size: 13.5pt;">1.0 Background</span></strong></p></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"><strong>1.1 Historical</strong></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">In the mid-1980’s, Interscan developed an instrument to be used in the clearance of structures treated with Vikane<sup>® </sup>gas fumigant. At the time, the reentry level was set at 10 ppm (parts-per-million). The measuring range of the instrument was 0-50 ppm, with an integral analog meter. The units were usually calibrated with span gas at a target level of 40 ppm.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"><span
id="more-89"></span>Some years later, the reentry level was lowered to 5 ppm. To accommodate this change, operation of the integral pyrolyzer (or furnace) was modified to produce better conversion of the SO<sub>2</sub>F<sub>2</sub> to SO<sub>2</sub>, and thus, improved sensitivity of the instrument. A procedure was subsequently introduced calling for more frequent calibration, within 30 days of use.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">Recent federal re-registration of this pesticide by the US EPA has once again lowered the reentry level—this time to 1 ppm. About one year prior to this label change, the span gas was lowered to a target level of 5 ppm.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"><strong>1.2 Purpose of this document and technical scope</strong></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">Although the Interscan was originally designed to detect levels of 10 ppm and subsequently modified to detect at 5 ppm, increased care in operation and maintenance of this instrument will effectively achieve satisfactory performance to the first division on the meter, 1 ppm.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">This document will focus on methods that will optimize instrument performance under these new operating conditions. Certain of these methods are subject to change as modifications (including digital meter kits) are made to your Interscan unit, and revisions to this document will be issued at that time. Detailed discussion of accuracy, resolution, and calibration is beyond the scope of this document.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"><strong><span
style="font-size: 13.5pt;">2.0 New Instrument Operating Procedures</span></strong></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"><strong>2.1 Zeroing the instrument</strong></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">2.1.1 Current procedures, as outlined in the GF-1900 instruction manual, call for zeroing the unit with ambient air, which is being drawn in by the integral sample pump. Whether one was operating in the 10 ppm or 5 ppm era, prudence would always dictate that this zeroing be done only in an environment that would be free from contamination with sulfuryl fluoride gas.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">2.1.2 Now, however, the slightest contamination might be enough to compromise the zero, and therefore the fumigant clearance reading.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">2.1.3 Best practice shall now be to use the following procedures to assure that only clean air, free from any sulfuryl fluoride gas, be utilized to zero the instrument. It is recommended to zero the instrument a minimum of 10 feet <strong>upwind</strong> from the fumigated structure and outside of carports, porches, or other areas with overhanging roofs attached to the fumigated structure.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">2.1.4 Current procedures, as outlined in the GF-1900 instruction manual, call for waiting until the READY light illuminates before zeroing the instrument. In addition, the user is cautioned to wait until the meter stops moving, before attempting to zero the instrument. Given the critical nature of the zero setting, initial meter stability must be especially emphasized, even if stating this instruction is technically nothing new. Thus, best practice shall now be as follows:</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">As before, wait until the READY light illuminates, but after this occurs, check that the meter is stable (needle steady and not moving) before attempting to zero the instrument. Depending on when the instrument was last used, this could take an extra few minutes.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">2.1.5 The new zeroing method, described in 2.1.3 and 2.1.4 shall be performed just before each clearance.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"><strong>2.2 Taking readings in the structure to be cleared</strong></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">2.2.1 Random motion imparted to the instrument, from walking around while holding it, could cause the meter to bounce around mechanically, rendering a reading of one division difficult. In addition, holding the instrument at odd angles may affect meter movement.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">2.2.2 Best practice shall now be to stop walking, hold the monitor parallel to the ground, and stand still while taking a reading.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"><strong>2.3 Interpreting a one ppm reading</strong></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">2.3.1 Users of the GF-1900 are well familiar with the difference between artificially induced spikes (often caused by excessive radio frequency interference) and true instrument response. A true instrument response is characterized by a smooth, steady rise of the meter needle.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">2.3.2 As such, best practice shall be to define a one ppm reading as a smooth, steady rise of the meter needle to a point coincidental with, or beyond the first meter division. To distinguish this from possible noise, this reading must persist for at least 5 seconds.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"><strong><span
style="font-size: 13.5pt;">3.0 Conclusions</span></strong></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">The move to a 1 ppm clearance level has put increased burdens on all of us: The fumigant manufacturer, the fumigator, the instrument company, and the regulators. Even the most sophisticated analyzers are pressed to the maximum to read 1 ppm, and these are priced at a point nearly ten times higher than the GF-1900.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">This Best Practices document, as well as subsequent mod kits and newer models of the Interscan sulfuryl fluoride monitor, will help our valued customers in their continuing efforts to provide safe and effective pest control by effectively achieving the 1 ppm clearance standard.</div> ]]></content:encoded> <wfw:commentRss>http://www.vikanemonitor.com/reading-1-ppm-on-legacy-interscan-sulfuryl-fluoride-monitors-model-gf-1900/feed/</wfw:commentRss> <slash:comments>0</slash:comments> </item> <item><title>ProFume&#174;</title><link>http://www.vikanemonitor.com/profume/</link> <comments>http://www.vikanemonitor.com/profume/#comments</comments> <pubDate>Sun, 15 Jan 2012 20:44:42 +0000</pubDate> <dc:creator>vikane.admin</dc:creator> <category><![CDATA[ProFume® Documents]]></category><guid
isPermaLink="false">http://www.vikanemonitor.com/index2.php/?p=86</guid> <description><![CDATA[<p>ProFume® Applicator Manual ProFume® Fact Sheet ProFume® Fumigation Warning Sign ProFume® HazMat Sheet ProFume® MSDS Sulfuryl Fluoride Pesticide Tolerance (EPA) &#160; Above links open pdf files</p> ]]></description> <content:encoded><![CDATA[<div><a
href="http://www.vikanemonitor.com/images/container_label_and_applicator_manual_for_profume_gas_fumigant.pdf" target="_blank"><span
style="font-family: Tahoma; font-size: 18pt;">ProFume<sup>®</sup> Applicator Manual</span></a></p><p><a
href="http://www.vikanemonitor.com/images/fact_sheet_for_profume_gas_fumigant.pdf" target="_blank"><span
style="font-family: Tahoma; font-size: 18pt;">ProFume<sup>®</sup> Fact Sheet</span></a></p><p><a
href="http://www.vikanemonitor.com/images/profume_fumigation_warning_sign.pdf" target="_blank"><span
style="font-family: Tahoma; font-size: 18pt;">ProFume<sup>®</sup> Fumigation Warning Sign</span></a></p><p><a
href="http://www.vikanemonitor.com/images/profume_hazmat_sheet.pdf" target="_blank"><span
style="font-family: Tahoma; font-size: 18pt;">ProFume<sup>®</sup> HazMat Sheet</span></a></p><p><a
href="http://www.vikanemonitor.com/images/profume_msds.pdf" target="_blank"><span
style="font-family: Tahoma; font-size: 18pt;">ProFume<sup>®</sup> MSDS</span></a></p><p><a
href="http://www.vikanemonitor.com/images/epa_federal_register_sulfuryl_fluoride_pesticide_tolerance.pdf" target="_blank"><span
style="font-family: Tahoma; font-size: 18pt;">Sulfuryl Fluoride Pesticide Tolerance (EPA)</span></a><a
href="http://www.adobe.com/products/acrobat/readstep2.html"><span
style="font-size: 10pt;"><img
src="http://www.adobe.com/products/acrobat/readstep2.html" alt="Get the Acrobat Reader" width="88" height="83" align="right" border="0" hspace="25" vspace="25" /></span></a></p><p>&nbsp;</p><div><span
style="font-size: 10pt;"><span
id="more-86"></span>Above links open pdf files </span></div></div> ]]></content:encoded> <wfw:commentRss>http://www.vikanemonitor.com/profume/feed/</wfw:commentRss> <slash:comments>0</slash:comments> </item> <item><title>Model GF-1900 Sulfuryl fluoride analyzer</title><link>http://www.vikanemonitor.com/model-gf-1900-vikane/</link> <comments>http://www.vikanemonitor.com/model-gf-1900-vikane/#comments</comments> <pubDate>Sun, 15 Jan 2012 20:42:13 +0000</pubDate> <dc:creator>vikane.admin</dc:creator> <category><![CDATA[Instruction Manuals]]></category><guid
isPermaLink="false">http://www.vikanemonitor.com/index2.php/?p=82</guid> <description><![CDATA[<p>Model GF-1900 Instruction Manual      (1.1 MB)  Click on above link to download pdf version of manual        </p> ]]></description> <content:encoded><![CDATA[<p><span
style="font-size: large;"><a
href="http://www.adobe.com/products/acrobat/readstep2.html"><img
class="alignright  wp-image-52" title="getacro_2" src="http://www.vikanemonitor.com/wp-content/uploads/2012/01/getacro_2.gif" alt="" width="122" height="115" /></a><a
href="http://www.vikanemonitor.com/images/sulfuryl_fluoride_monitor_manual_rev_c.pdf">Model GF-1900 Instruction Manual</a>      (1.1 MB) </span></p><p><span
id="more-82"></span>Click on above link to download pdf version of manual        </p> ]]></content:encoded> <wfw:commentRss>http://www.vikanemonitor.com/model-gf-1900-vikane/feed/</wfw:commentRss> <slash:comments>0</slash:comments> </item> <item><title>When a sulfur dioxide scrubber must be used with the ProFume monitor</title><link>http://www.vikanemonitor.com/when-a-sulfur-dioxide-scrubber-must-be-used-with-the-profume-monitor/</link> <comments>http://www.vikanemonitor.com/when-a-sulfur-dioxide-scrubber-must-be-used-with-the-profume-monitor/#comments</comments> <pubDate>Sat, 14 Jan 2012 02:15:52 +0000</pubDate> <dc:creator>vikane.admin</dc:creator> <category><![CDATA[Best Practices]]></category> <category><![CDATA[Calibration, Maintenance, and Performance]]></category><guid
isPermaLink="false">http://www.vikanemonitor.com/index2.php/?p=51</guid> <description><![CDATA[<p>When A Sulfur Dioxide Scrubber Must Be Used With The ProFume® Monitor(197 kB) Click on above link to download the article (in pdf format) &#160;</p> ]]></description> <content:encoded><![CDATA[<div><a
href="http://www.adobe.com/products/acrobat/readstep2.html"><img
class="alignright  wp-image-52" title="getacro_2" src="http://www.vikanemonitor.com/wp-content/uploads/2012/01/getacro_2.gif" alt="" width="122" height="115" /></a><a
href="http://www.vikanemonitor.com/images/when_a_sulfur_dioxide_scrubber_must_be_used_with_the_profume_monitor.pdf">When A Sulfur Dioxide Scrubber Must Be Used With The ProFume<sup>®</sup> Monitor</a>(197 kB)</p><div></div><div><span
id="more-51"></span>Click on above link to download the article (in pdf format)</div></div><p>&nbsp;</p> ]]></content:encoded> <wfw:commentRss>http://www.vikanemonitor.com/when-a-sulfur-dioxide-scrubber-must-be-used-with-the-profume-monitor/feed/</wfw:commentRss> <slash:comments>0</slash:comments> </item> <item><title>How using a 5 ppm calibration standard affects the accuracy of legacy Interscan GF-1900 sulfuryl fluoride monitors</title><link>http://www.vikanemonitor.com/how-using-a-5-ppm-calibration-standard-affects-the-accuracy-of-legacy-interscan-gf-1900-sulfuryl-fluoride-monitors/</link> <comments>http://www.vikanemonitor.com/how-using-a-5-ppm-calibration-standard-affects-the-accuracy-of-legacy-interscan-gf-1900-sulfuryl-fluoride-monitors/#comments</comments> <pubDate>Sat, 14 Jan 2012 02:14:05 +0000</pubDate> <dc:creator>vikane.admin</dc:creator> <category><![CDATA[Calibration, Maintenance, and Performance]]></category><guid
isPermaLink="false">http://www.vikanemonitor.com/index2.php/?p=49</guid> <description><![CDATA[<p>Defining Our Terms As defined in the ANSI/ISA–51.1–1979 (R1993) standard entitled Process Instrumentation Terminology, “Accuracy” is the degree of conformity of an indicated value to a recognized accepted standard value, or ideal value. “Accuracy rating” is a number or quantity that defines a limit that&#8230; <a
class="more-link" href="http://www.vikanemonitor.com/how-using-a-5-ppm-calibration-standard-affects-the-accuracy-of-legacy-interscan-gf-1900-sulfuryl-fluoride-monitors/">Continue reading <span
class="meta-nav">&#8594;</span></a></p> ]]></description> <content:encoded><![CDATA[<div
style="margin: 0in 0in 0pt;"><strong><span
style="font-family: Courier New; font-size: 14pt;"><span
style="font-family: Tahoma; color: #800080;">Defining Our Terms</span><br
/> </span></strong><br
/> As defined in the <span>ANSI/ISA–51.1–1979 (R1993) standard entitled <em>Process Instrumentation Terminology</em>, </span></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt 0.5in;"><strong>“Accuracy” </strong>is the degree of conformity of an indicated value to a recognized accepted standard value, or ideal value.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt 0.5in;"><strong>“Accuracy rating”</strong> is a number or quantity that defines a limit that errors will not exceed when a device is used under specified operating conditions. Accuracy rating includes the combined effects of conformity, hysteresis, dead band, and repeatability errors.</div><div
style="margin: 0in 0in 0pt;"><strong><span
style="font-family: Courier New; font-size: 14pt;"><span
style="color: #800080;"><br
/> <span
style="font-family: Tahoma;">Expressing Accuracy Rating</span></span></span></strong></div><div
style="margin: 0in 0in 0pt 0.5in;"></div><div
style="margin: 0in 0in 0pt 0.5in; text-indent: -0.5in;">Two common methods of expressing accuracy rating are<span
id="more-49"></span></div><div
style="margin: 0in 0in 0pt 0.5in; text-indent: -0.5in;"></div><ul
style="margin-top: 0in;" type="disc"><li
style="margin: 0in 0in 0pt;">Percent of scale length (percent of full scale)</li><li
style="margin: 0in 0in 0pt;">Percent of actual output reading</li></ul><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">Traditionally, expressing accuracy rating with percent of full scale has been used with analog instruments. On legacy Interscan Vikane<sup>®</sup> monitors, accuracy rating is ±2% of full scale. Since the full scale range is 0-50 ppm, any reading is accurate ±1 ppm.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">With digital instruments, it is more common to express accuracy rating with percent of reading, often adding the inherent error of the least significant digit. Thus, one might encounter the specification of ±2% of reading ±1 least significant digit. <span
style="font-family: Arial; font-size: 10pt;"><span
style="font-size: 10pt;">[The least significant digit is the lowest digit in a number, located at the far right of a string.]</span></span></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">In such a case, if the digital range were 0-50 ppm, at a reading of 1 ppm, the accuracy would be 1 ppm ± 0.02 ppm ±1 ppm (meaning that the true value could be between 0 &#8211; 2.02 ppm).</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">If the digital range were 0-50.0 ppm, at a reading of 1 ppm, the accuracy would be 1 ppm ± 0.02 ppm ± 0.1 ppm (meaning that the true value could be between 0.88 &#8211; 1.12 ppm).</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"><p><span
style="font-family: Tahoma;"><strong><span
style="color: #800080; font-size: 14pt;">The Influence of the Calibration Standard</span></strong></span></p><p>However, in gas detection, most instruments, including all instruments used to detect Vikane<sup>®</sup>, must be calibrated against a known standard. Thus, these instruments are reference methods, rather than absolute methods.</p></div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">By all rights, the accuracy of the calibration standard should be taken into account when discussing the accuracy of a gas detection instrument, but in practice, this is done more by implication than directly. An instrument manufacturer may reveal in some footnote that measurement accuracy is limited to the accuracy of the calibration standard, but then proceed as if this does not really matter.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">In other words, although a disclaimer may be presented, all accuracy specs will deal with inherent matters of the instrument only. In fact, the error in calibration standard accuracy would be additive, and it is likely that this would add another ±2 percent to the mix. Fortunately, with the mandated 5 ppm calibration standard, this yields an additional error of only 0.1 ppm.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">But, the 5 ppm calibration standard improves accuracy in one other way:</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">All other things being equal (but, we will find that they are NOT) it is considered best practice to calibrate a gas analyzer at somewhere between 50-85% of the full-scale value. That is why a 40 ppm standard was long used for the Vikane<sup>®</sup> monitor.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">However, it is also considered best practice to calibrate at a value reasonably close to the levels at which you will be measuring. Hence, the introduction of the 5 ppm calibration standard. Note that even if a 1 ppm standard were available, it would be unwise to calibrate an instrument so close to the bottom of its range.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;">Consider that the ±1 ppm accuracy spec was based on a full scale range of 0-50 ppm. Arguably, since the majority of clearance measurements will be made in the range of 0-5 ppm, and the unit will be calibrated with a 5 ppm standard, some allowance should be made for this compression of scale.</div><div
style="margin: 0in 0in 0pt;"></div><div
style="margin: 0in 0in 0pt;"><p>By conventional reasoning, a true 0-5 ppm range instrument would have an accuracy of ±0.1 ppm. And while one cannot hold that our 0-50 ppm unit, pressed into service as a quasi 0-5 ppm unit—by virtue of the new calibration standard—is a true 0-5 ppm instrument, some accuracy benefit should still ensue in this very special case.</p></div><div
style="margin: 0in 0in 0pt;"><span
style="color: #800080; font-size: 14pt;"><strong><span
style="font-family: Tahoma;"><br
/> It All Comes Down To This</span></strong></span></div><div
style="margin: 0in 0in 0pt;">A very conservative approach would be to average the two ranges, giving a “virtual” measuring range of 0-27.5 ppm. As such, the accuracy would be ±0.55 ppm—a significant improvement.</div><div
style="margin: 0in 0in 0pt;"></div><p>It is stipulated that some analytical purists may take issue with our “virtual” measuring range argument, but then analytical purists—happily ensconced in their laboratories—do not have to clear structures, subject to extremely demanding environmental regulations.</p> ]]></content:encoded> <wfw:commentRss>http://www.vikanemonitor.com/how-using-a-5-ppm-calibration-standard-affects-the-accuracy-of-legacy-interscan-gf-1900-sulfuryl-fluoride-monitors/feed/</wfw:commentRss> <slash:comments>0</slash:comments> </item> </channel> </rss>
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