text: Virtual Field Trip Extravaganza - "Folklore and Fables" October 12, 2012 Do your students love to tell stories? Have they ever seen a story be told by a master storyteller? This October, our Virtual Field Trip Extravaganza Series will focus on "Folklore and Fables". We'll hear outrageous stories brought to life through readings and performances by expert storytellers and authors. We'll explore myths and legends behind the fables and even experience stories through puppetry. Not familiar with virtual field trips? No problem. A virtual field trip happens in the comfort of your classroom, library or auditorium via the power of live video. Review clips from previous Extravaganzas here. All of the field trips will be streamed live on this page, so grab a computer and get ready for some fun for your class! Schedule: 9:00 am CDT A National Theater Company of One: "Christopher Columbus" (geared towards grade levels 6-12) This program is a live first-person presentation of Christopher Columbus discussing his first voyage and sharing a map of his journey. We'll also discuss the historical-based character and separate myth from fact. 10:00 am CDT Houston Audubon: "Stories from the Earth" (geared towards grade levels 1-8) Listen to stories from our ancestors while learning about the amazing creatures that call Earth "home". We will unravel some of the most well-known folktales and listen to some lesser-known tales that teach us the lessons of "stewardship" for our planet. Live birds and other animals bring this program to life. 11:00 am CDT A National Theater Company of One: "Johnny Appleseed" (geared towards grade levels 3-5) Hear Johnny Appleseed tell you about his family, his beginnings and his importance on the western frontier. Along the way, he will engage you with funny stories and maybe convince you to buy some of his apple seedlings for a penny. 12:00 pm CDT Cleveland Museum of Art : "Gods and Heroes of the Maya" (geared towards grade levels 6-12) The Maya Popol Vuh (Council Book) relates tales of the Hero Twins who make the world safe for the arrival of human beings. During this lesson, students explore this creation myth and other aspects of the Maya culture by examining artifacts from The Cleveland Museum of Art. 1:00 pm CDT Center for Puppetry Arts: "Little Red Hen & the Grain of Wheat" (geared towards grade levels K-5) This classic tale comes to life through an interactive performance led by puppeteer Jeffrey Zwartjes. Colorful hand puppets tell the story of a hen who finds a grain of wheat. She wants to harvest the wheat but none of the other barnyard animals will help her, so she decides to do it all herself. Will Little Red Hen share her bounty with the other animals? Your will students decide and will learn lessons of hard work. 2:00 pm CDT Houston Audubon: "Stories that SOAR: Birds in Mythology, Legend, and Storytelling" (geared towards grade levels K-5) Hear stories and legends from around the world as we explore the history of our most famous or infamous birds. Meet live birds as we go back in time to discover fact and fiction about our feathered friends.


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REVISION F March 1992
All sections and exhibits of the Arizona Testing Manual for Air Pollutant Emissions have been updated or otherwise amended in this revision (Revision F).
TABLE OF CONTENTS Section
1.0 1.1 1.2.1 1.2.2 Exhibit 1.2-1 Exhibit 1.2-2
Introduction Performance Test Planning and Approval Agency Observer Requirements Visible Emissions Evaluator Training and Certification Performance Test Plan Requirements Process and Control Equipment Operating Parameters To Be Recorded At Least Every 30 Minutes Quality Assurance Provisions Quality Assurance Procedures Equipment Maintenance and Calibration Quality Assurance Audits OAQ Observer Activities Test Procedures Test Documentation and Reporting Performance Test Report Outline Test Report Review
1 1 2 2 3 6
1.3 1.3.1 1.3.2 1.3.3 1.4.1 1.4.2 1.4.3 Exhibit 1.4.3-1 1.4.4 Exhibit 1.4.4-1
7 7 7 7 7 7 8 9 11 12
Compliance Test Report
TABLE OF CONTENTS (CONT.) Section
Listing of Environmental Protection Agency Reference Test Methods for Source Emissions, 40 CFR 60, Appendix A, updated thru 6/30/91 Listing of Environmental Protection Agency Performance Specification Test Procedures for Continuous Emissions Monitoring Systems: 40 CFR 52, Appendices D & E; 40 CFR 60, Appendix B, updated thru 6/30/91 Listing of Environmental Protection Agency Quality Assurance RequireMents for Gas Continuous Emissions Monitoring Systems Used For Compliance Determinations, 40 CFR 60, Appendix F, updated thru 6/30/91 Listing of Environmental Protection Agency Test Methods for Hazardous Air Pollutant Emissions, 40 CFR 61, Appendix B, updated thru 6/30/91 Listing of Environmental Protection Agency Quality Assurance Procedures for Testing Emissions of Hazardous Air Pollutants, 40 CFR 61, Appendix C, updated thru 6/30/91 Arizona Emission Test Method Al
The Office Air Quality (OAQ), acting for the Director of the Department of Environmental Quality, is responsible for determining each regulated air pollution source's capability and continuing ability to comply with air pollution source's emission rules, adopted by the Director pursuant to Arizona Revised statutes ?49 - 401 et seq.; and any terms of conditional permits issued by the Arizona Air Pollution Control Hearing Board. This applies to all sources under the jurisdiction of the Department in matters of air pollution control. Performance tests, and/or visible emissions observations by agency personnel, are required to assure that sources are compliant with all applicable emission limitations at all major emission points before air pollution source operating permit are issued or renewed. If OAQ engineering analysis and field inspection provide defensible assurance of compliance, these requirements may be waived. OAQ may also require additional performance testing at anytime during the permit period when lack of compliance with the applicable rules is demonstrated or suspected. 1.1 PERFORMANCE TEST PLANNING AND APPROVAL
Performance testing for regulated pollutants is required of all sources subject to air pollution control for verification of compliance with applicable Arizona rules, unless compliance can be assured and documented by a department engineering analysis confirmed by on-site inspections. Regulated air pollution sources shall conduct any required compliance verification performance testing in accordance with OAQ approved methods. All performance testing and field evaluations to determine the compliance status of regulated air pollution sources is subject to onsite verification by qualified OAQ representatives. Advance notice of performance testing shall be given to OAQ in accordance with A.A.C. R18-2-312.D. Sources subject to performance testing must also provide test facilities and test plans in accordance with A.A.C. R18-2-312. OAQ approval of test plans and any variations from approved test methods is required. Failure to obtain prior approval for plans and any variations from approved methods may result in rejection of the performance testing results. Requirements for performance test plans are outlined in Exhibit 1.2-1. In order to work out the logistics of each test, and to arrange for an OAQ observer to be present at the test, a pre-test meeting should be arranged with OAQ at least 14 days before testing is to occur.
Major sources having multiple emission points must submit facility test schedules assuring annual testing of major emission points and rotational testing of minor emissions points as required by permit conditions. Rotational testing of identical or essentially similar air pollution control devices may also be authorized through permit conditions. 1.2.1 AGENCY OBSERVER REQUIREMENTS
OAQ representatives assigned to performance test verifications are required to have a degree in engineering or a related air pollution control discipline from an accredited college, or its equivalent. Each OAQ observer undergoes ongoing technical training to assure initial and continuing proficiency. Each observer is also required to maintain current certification as a visible emissions evaluator. 1.2.2 VISIBLE EMISSIONS EVALUATOR TRAINING AND CERTIFICATION
Approved training in visually measuring emissions is necessary for proper use of EPA Reference Method 9 (40 CFR 60, Appendix A). Opacity measurement training may be provided by OAQ, or through another OAQ-recognized training program. Certification testing will be conducted by OAQ personnel or OAQrecognized training personnel. Training course and certification costs for persons other than OAQ personnel are not the responsibility of ADEQ. Equipment utilized for visible emissions evaluator training must be calibrated, operated, and maintained in accordance with the procedures contained in EPA Reference Method 9 (40 CFR 60, Appendix A). To receive initial certification as a visible emissions evaluator, a candidate must successfully attend an OAQ or OAQrecognized training school on the theory and practice of visible emissions evaluation, and pass the field certification test for measuring visible emissions within six months thereafter. To maintain certification, a person must retake a recognized training course once every two years and repass he field certification test once every six months.
Exhibit 1.2-1 PERFORMANCE TEST PLAN REQUIREMENTS The information specified below must be submitted to the Compliance Unit of the Office of Air Quality at least 14 working days prior to the scheduled test date. This information is required in order to insure that proper test methods and procedures are utilized. The Compliance Unit will review the test plan, and in the event of any deficiencies or comments concerning the plan, will contact the company to discuss the test plan. Submittal of this information will minimize the possibility of a test being rejected as a result of improper sampling or data collection procedures. All testing shall be performed in strict accordance with the procedures, specified in an OAQ approved test plan. Any proposed variation in the sampling or analytical procedures must receive approval from OAQ Compliance prior to testing. Appropriate chain of custody procedures must be followed during the sampling and analysis. The following information should be included in the performance test plan: 1. Source Information: A. Name (including serial number of equipment), address, and location of the facility being tested. B. Responsible persons at the facility and telephone number. Testing Firm Information: A. Name and address of the firm conducting the testing. B. Responsible person at the testing firm and telephone number. Sampling Equipment: A. A description of the emission sampling equipment including a schematic diagram of the sampling train.
4. Procedures: A. Types of pollutants to be sampled. B. A description of the sampling and analysis procedures. C. Documentation for any proposed variations from OAQ approved procedures. 5. Emission Point Information: A. A diagram of the stack showing the dimensions, and the configuration of the sampl1ng location, location of continuous emission monitor (CEM) probes, and the distances to the nearest upstream and downstream flow interferences.
A cross-sectional sketch of the stack at the sampling location, showing the locations of the sampling traverse points. Estimated flue gas conditions at the sampling location, including temperature, moisture content, and velocity.
Process Information: A. Schematic diagram identifying gas flow from origination point to exit point, including identification of all control devices, fans and bypasses. B. Other specific process information may be required on a case-by-case basis. Process Equipment: A. A description of the process equipment, including a process flow sheet. B. Type and quantity of raw materials, catalysts, and products being used or produced in the process. C. Maximum rated capacity of the process. D. Actual maximum operating of the process. E. Operating capacity during the previous six-month period. F. Process data being monitored and recorded to insure representative operation throughout the test, including during the sampling interval. G. Normal process operating schedule during a 24-hour period. H. Normal maintenance schedule for this process. I. Types of fuel used in production. Control Equipment: A. Description of emission control system, including the types of control equipment, manufacturer of control equipment, the rated capacity and efficiency of the control equipment. B. Data to be monitored and recorded to insure representative operation of the control equipment during testing and the sampling period for recording. C. Minimum acceptable values of all control devices parameters such as flow rates, pressure drops, temperature, and voltage of electrical input. D. Description of any preconditioning of gases used with control equipment. E. Normal maintenance schedule on control equipment for the previous year.
Data Sheets: A. Copies of all field data sheets to be used during the test, including data sheets to record process and control equipment parameters. Chain of Custody: A. A description of the procedures that will be followed to maintain the integrity of the samples collected. B. Copies of chain of custody seals and data sheets. Quality Control: (The following items should be available to the OAQ observer of the performance test prior to the start of the test.) A. Calibration sheets for the dry gas meter, pitot tube, nozzle, and other equipment requiring calibration. B. Quality assurance control charts for the analytical procedures to be used in the analysis of the test samples. C. A list of preweighted filters to be used during particulate emissions testing.
Exhibit 1.2-2 PROCESS AND CONTROL OPERATING PARAMETERS TO BE RECORDED AT LEAST EVERY 30 MINUTES ASPHALT PLANTS Process Rate Recycle Rate Drum Temperature POWER PLANTS Generation Rate Coal Feed Rate Opacity, SO2, NOx and %CO 2 or %O2 from CEM's (record at least every 15 minutes) Coal Analysis OTHER SOURCES Process Rate Other parameters as applicable ---------------------------------------------------------------------ESP Operating voltage (per field) Operating current (per field) Spark rate Cleaning cycle Fan current or speed SCRUBBER Pressure drop Water flow rate Water supply pressure Fan speed or current Other parameters such as pH values, as applicable BAGHOUSE Pressure drop (total) Pressure drop (each compartment) Number, type, and temperature range of bags Damper position Fan current or speed Cleaning cycle
1.3 1.3.1
The applicable procedures contained in the Quality Assurance Handbook for Air Pollution Measurement Systems, Volume III Stationary Source Specific Methods, incorporated herein by reference, shall be used. 1.3.2. EQUIPMENT MAINTENANCE AND CALIBRATION
Performance test equipment, including instrumentation, must be maintained in accordance with manufacturers' instructions and good engineering practice. Instrumentation for measurement of pertinent physical parameters shall be currently calibrated with traceability to documented reference standards or procedures. Verification of such maintenance and calibration must be documented in each test record. Performance of all calibration and control checks required by the approved test methods must be documented. 1.3.3. QUALITY ASSURANCE AUDITS
Audits of the sampling equipment and of the analytical techniques used may be required at any time during performance testing. The OAQ may use the results of such audits to determine the acceptability o f test results. 1.4.1. OAQ OBSERVER ACTIVITIES observe all performance testing analysis may also be performed. are recorded by the observer at testing. A summary of the field
OAQ personnel are assigned to activities. Observation of laboratory Visible emissions observations appropriate times during performance observations is documented. 1.4.2. TEST PROCEDURES
The procedures used during performance tests and subsequent sample analysis shall conform to that agreed upon in an approved test plan and/or at a pre-test meeting. When necessary, the OAQ observer may authorize minor modifications to agreed procedures at the time of the test. The number of test runs required shall be in accordance with A.A.C. R18-2-312.F.
The OAQ observer may initial field data sheets, and may require that copies be provided on-site. Preliminary results may be required to be furnished on-site if feasible, or by telephone within three days of completion of the testing. The final test report shall be submitted to the OAQ within four weeks after the completion of testing. The test report will contain, at a minimum, the information listed in Exhibit 1.4.3-1. All pages of the report must be numbered to maximize it usefulness. All test samples must be maintained and be available to OAQ upon request for a period of one year after testing. A complete copy of all test records shall be retained by the source for a minimum period of three (3) years. This record shall include all applicable documents noted in this manual.
Exhibit 1.4.3-1 PERFORMANCE TEST REPORT OUTLINE GENERAL 1. Plant name and location. 2. Source sampled. 3. Testing company or agency, name and address. CERTIFICATION 1. Certification by team leader. 2. Certification by reviewer (e.g., P.E.). TABLES OF CONTENTS (Include page numbers) INTRODUCTION 1. Test purpose. 2. Test location, type of process. 3. Test dates. 4. Pollutants tested. 5. Observers' names (source and OAQ AQD). 6. Any other important background information. SUMMARY OF RESULTS 1. Emission results. 2. Process data. 3. Allowable emissions. 4. Discussion of errors, both real and apparent. SOURCE OPERATION 1. Description of source and control devises. 2. Process and control equipment diagram. 3. Process and control equipment data. 4. Representativeness of materials and operation. 5. Demonstration of any specially-required operation. SAMPLING AND ANALYSIS PROCEDURES 1. Sampling port location and cross-section with dimensions. 2. Sampling port description, including labeling system. 3. Sampling train description. 4. Description of sampling procedures, and any deviations from standard procedures . 5. Description of analytical procedures, and any deviations from standard procedures.
Exhibit 1.4.3-1 (Cont.) APPENDICES 1. Complete results with example calculations. 2. Copies of original field and laboratory data sheets. 3. Copies of original production data signed by plant official. 4. Test log. 5. Calibration procedures and results. 6. Project participants and titles. 7. Related correspondence.
Upon the submittal of the final test report, the report is checked for completion, and the results are checked for accuracy and compliance with the applicable emission limits. The results of this review is documented on Exhibit 1.4.4-1. The source will be notified of the results of the review and any additional information or testing that may be required.
Exhibit 1.4.4-1 ARIZONA DEPARTMENT OF ENVIRONMENTAL QUALITY OFFICE OF AIR QUALITY COMPLIANCE TEST REPORT Name of Company______________________________ County___________________
Source Tested___________________________________________________________ Person Submitting Test Report___________________________________________ Date(s) of Test(s)______________________________________________________ Circle One: PASS FAIL Process Rate___________________ Plant Emission Rates____________________________________________________ Maximum Allowable Emission Rate_________________________________________ Review of Test Method___________________________________________________ Review of Test Calculations_____________________________________________ ________________________________________________________________________ ________________________________________________________________________ Report Demonstrates Compliance with Applicable Emission Standards ________________________________________________________________________ ________________________________________________________________________ Reviewer ____________________________________ Date_____________________ Comments (Precision and accuracy of replicate tests, percent isokinetic sampling, operating anonmalies): ________________________________________________________________________ ________________________________________________________________________ ________________________________________________________________________ cc: ___ Source Permit File ___ Permit Engineer ___ Source
SECTION 2.0 Listing of Environmental Protection Agency Reference Test Methods for Source Emissions 40 CFR 60, Appendix A Method 1 1A Revised 07/01/89 07/01/89 Subject Sample and Velocity Traverses for Stationary Sources Sample and Velocity Traverses for Stationary Sources with Small Stacks or Ducts Determination of Stack Velocity and Volumetric Flow Rate (Type S Pitot Tube) Measurement of Gas Volume Through Pipes and Small Ducts Determination of Exhaust Gas Volume Flow Rate from Gasoline Vapor Incinerators Determination of Stack Gas Velocity and Volumetric Flow Rate in Small Stacks or Ducts (Standard Pitot Tube) Measurement of Gas Volumetric Flow Rates in Small Pipes and Ducts Gas Analysis for Carbon Dioxide, Excess Air, and Dry Molecular Weight Determination of Oxygen and Carbon Dioxide Concentration in Emissions From Stationary Sources (Instrumental Analyzer Procedure) Gas Analysis for the Determination of Emission, Rate Correction Factor or Excess Air
11/14/90 Direct 11/14/90
07/01/89 02/14/90 07/01/89
SECTION 2.0 (CONT.) Method 4 5 5A Revised 11/14/90 11/14/90 11/14/90 Subject Determination of Moisture in stack Gases Determination of Particulate Emissions from Stationary Sources Determination of Particulate Emissions from the Asphalt Processing and Asphalt Roofing Industry Determination of Non-Sulfuric Acid Particulate Matter From Stationary Sources Determination of Particulate Matter Emissions from Positive Pressure Fabric Filters Determination of Particulate Matter from the Wool Fiberglass Insulation Manufacturing Industry Determination of Nonsulfate Particulate Matter From Stationary Sources Determination of Particulate Emissions from Wood Heaters from a Dilution Tunnel Sampling Location Determination of Particulate Emissions from Wood Heaters from a Stack Location Determination of Sulfur Dioxide Emissions from Stationary Sources Determination of Sulfur Dioxide, Moisture, and Carbon Dioxide from Fossil Fuel Combustion Sources Determination of Sulfur Dioxide and Carbon Dioxide Daily Average, Emissions from Fossil Fuel Combustion Sources
07/01/89 07/01/89
11/14/90 11/14/90
SECTION 2.0 (CONT.) Method 6C Revised 11/02/89 Subject Determination of Sulfur Dioxide Emissions from Stationary Sources (Instrumental Analyzer Procedure) Determination of Nitrogen Oxide Emissions from Stationary Sources Determination of Nitrogen Oxide Emissions from Stationary Sources-Ion Chromatographic Method Determination of Nitrogen Oxide Emissions from Stationary SourcesUltraviolet Spectrophotometry Determination of Nitrogen Oxide Emissions from Stationary SourcesAlkaline -Permanganate/Colorimetric Method Determination of Nitrogen Oxide Emissions from Stationary SourcesAlkaline -Permanganate/Ion Chromatographic Method Determination of Nitrogen Oxides Emissions from Stationary Sources (Instrumental Analyzer Procedure) Determination of Sulfuric Acid Mist Sulfur Dioxide Emissions from Stationary Sources Visual Determination of the Opacity of Emissions from Stationary Sources Determination of the opacity of Emissions from Stationary Sources Remotely by LIDAR Determination of Carbon Monoxide Emissions from Stationary Sources
9 Alt1
11/14/90 07/01/89
Alternate Method 1 (Formerly Method 9A)
SECTION 2.0 (CONT.) Method lOA Revised 11/02/89 Subject Determination of Carbon Monoxide Emissions in Certifying Continuous Emission Monitoring Systems at Petroleum Refineries Determination of Carbon Monoxide Emissions from stationary Sources Determination of Hydrogen Sulfide Content of Fuel Gas Streams in Petroleum Refineries Determination of Inorganic Lead Emissions from Stationary Sources Determination of Total Fluoride Emissions from Stationary SourcesSOADNS Zirconium Lake Method Determination of Total Fluoride Emissions from Stationary SourcesSpecific Ion Electrode Method Determination of Fluoride Emissions from Potroom Roof Monitors for Primary Aluminum Plants Determination of Hydrogen Sulfide, Carbonyl Sulfide, and Carbon Disulfide Emissions from Stationary Sources Determination of Total Reduced Sulfur Emissions from Sulfur Recovery Plants in Petroleum Refineries Semi-continuous Determination of Sulfur Emissions from Stationary Sources Determination of Total Reduced Sulfur Emissions from Stationary Sources (Impinger Technique)
lOB 11
07/01/89 11/14/90
11/14/90 07/01/89
SECTION 2.0 (CONT.) Method 16B 17 Revised 07/01/89 11/14/90 Subject Determination of Total Reduced Sulfur Emissions from Stationary Sources Determination of Particulate Emissions from Stationary Sources (In-Stack Filtration Method) Measurement of Gaseous Organic Compound Emissions by Gas Chromatography Determination of Sulfur Dioxide Removal Efficiency and Particulate, Matter Sulfur Dioxide, and Nitrogen Oxides Emission Rates Determination of Nitrogen Oxides, Sulfur Dioxide, and Diluent Emissions from Stationary Gas Turbines Determination of Volatile Organic Compounds Leaks Visible Determination of Fugitive Emissions from Material Processing Sources Determination of Polychlorinated Debenzo-p-Dioxins Polychlorinated Dibenzofurans from Stationary Sources Determination of Volatile Matter Content, Water Content, Density, Volume Solids, and Weight Solids of Surface coatings Determination of Volatile Matter Content and Density of Printing Inks and Related Coatings Determination of Total Gaseous Nonmethane Organic Emissions as Carbon
21 22
11/14/90 07/01/89
SECTION 2.0 (CONT.) Method 25A Revised 07/01/89 Subject Determination of Total Gaseous Organic Concentration Using a Flame Ionization Analyzer Determination of Total Gaseous Organic Concentration Using a Nondispersive Infrared Analyzer Determination of Hydrogen Chloride Emissions from stationary Sources Determination of Vapor Tightness of Gasoline Delivery Tank Using PressureVacuum Test Certification and Auditing of Wood Heaters Measurement of Air to Fuel Ratio and Minimum Achievable Burn Rates for Wood-Fired Appliances
26 27
02/13/91 07/01/89
07/01/89 11/19/90
SECTION 3.0 Listing of Environmental Protection Agency Performance Specification Test Procedures for Continuous Emissions Monitors 40 CFR 52. Appendix D* Determination of Sulfur Dioxide Emissions from Stationary Sources by Continuous Monitors. 40 CFR 52. Appendix E* Performance Specifications and Specification Test Procedures for Monitoring Systems for Effluent Stream Gas Volumetric Flow Rate. 40 CFR 60. Appendix B Performance Specifications 1 Last Revised 11/14/90 Subject Specifications and Test Procedures for Opacity Continuous Emission Monitoring Systems in Stationary Sources Specifications and Test Procedures for Sulfur Dioxide and Nitrogen Oxides Continuous Emission Monitoring Systems in Stationary Sources Performance Specifications and Test Procedures for Oxygen and Carbon Dioxide Continuous Emission Monitoring Systems in Stationary Sources
*These appendices were added to 40 CFR 52 in 02/06/75. No revisions were made thru 06/30/91.
SECTION 3.0 (CONT.) Performance Specifications 4 Last Revised 08/17/87 Subject Specifications and Test Procedures for Carbon Monoxide Continuous Emission Monitoring Systems in Stationary Sources Specification and Test Procedures for Carbon Monoxide Continuous Emission Monitoring Systems in Stationary Sources Specifications and Test Procedures for Total Reduced Sulfur Continuous Emission Monitoring Systems in Stationary Sources Specifications and Test Procedures for Continuous Emission Rate Monitoring Systems in Stationary Sources Specifications and Test Procedures for Hydrogen Sulfide Continuous Emission Monitoring Systems in Stationary Sources
SECTION 4.0 Listing of Environmental Protection Agency Quality Assurance Requirements for Gas Continuous Emissions Monitoring Systems Used For Compliance Determination 40 CFR 60. Appendix F Procedure 1 Last Revised 02/11/91 Subject Quality Assurance Requirements For Gas Continuous Emission Monitoring Systems Used For Compliance Determination
SECTION 5.0 Listing of Environmental Protection Agency Test Methods For Hazardous Air Pollutants 40 CFR 61, A22endix B Method 101 Last Revised 09/23/88 Subject Determination of Particulate and Gaseous Mercury Emissions from ChloroAlkali Plants-Air streams Determination of Particulate and Gaseous Mercury Emissions from Sewage Sludge Incinerators Determination of Particulate and Gaseous Mercury Emissions from ChloroAlkali Plants Hydrogen Streams Beryllium screening Method Determination of Beryllium Emissions from stationary Sources Determination of Mercury in Wastewater Treatment Plant Sewage Sludges Determination of Vinyl Chloride from stationary Sources Determination of Vinyl Chloride Content of Inprocess Wastewater Samples, & vinyl Chloride Content of polyvinyl Chloride Resin, Slurry, Wet Cake, and Latex Samples
103 104 105 106 107
12/09/83 09/23/88 09/23/88 09/23/88 09/23/88
SECTION 5.0 (CONT.) Method 107A Last Revised 09/23/88 Subject Determination of Vinyl Chloride Content of Solvents, Resin-Solvent Solution, Polyvinyl Chloride Resin, Resin Slurry, Wet Resin, and Latex Samples Determination of Particulate and Gaseous Arsenic Emissions Determination of Arsenic Content in Ore Samples From Nonferrous Smelters Determination of Arsenic Content in Ore Samples from Nonferrous Smelters (> 10?g As/ml concentration) Determination of Arsenic Content in Ore Samples from Nonferrous Smelters (< 10?g As/ml concentration)
05/31/90 05/31/90 05/31/90
SECTION 6.0 Listing of Environmental Protection Agency Quality Assurance Procedures for Hazardous Air Pollutants Emission Testing 40 CFR 61, Appendix C* Procedure 1 2 Subject Determination of Adequate Chromatographic Peak Resolution Procedure for Field Auditing Gas Chromatographic Analysis
*Appendix C was added to 40 CFR 61 on 09/07/82. No changes or additions were made to this appendix through 06/30/91.
SECTION 7.0 A1. ARIZONA EMISSION TEST METHOD A1 Determination of Particulate Emissions from Stationary Sources in the Presence of Sulfuric Acid Mist and Sulfur Oxides Principle Particulate matter is withdrawn isokinetically from the source and collected on a glass fiber filter. The temperature of the probe and filter is maintained above the dewpoint of water and sulfuric acid mist. The solid particulate mass is determined gravimetrically after removal of water and sulfuric acid by solvent extraction with acetone-heptane. A1.1.1 Sulfuric acid mist, sulfur trioxide, and arsenic are collected in an impinger train, and the amount determined by chemical analysis. The sulfuric acid mist in the solvent extract is also determined by chemical analysis. Sulfur dioxide is oxidized and collected in the impinger train. Applicability The method is applicable for the determination of solid particulate emissions as well as condensible sulfates from stationary sources where the emissions contain high levels of sulfuric acid mist and sulfur oxides. A1.3 Apparatus and Reagents The basic sampling train is the same as for EPA Method 5 described in APTO-O581, "Construction Details of Isokinetic Source Sampling Equipment." Commercial models of this sample train are available or can be fabricated. (See Figure 1 for train used.) The sample train is modified to include five impingers and a filter between the first and second impingers. The filterbox is capable of being heated to 350?F (177?C).All surfaces in contact with the gases are of a chemically inert material with the exception of the probe nozzle. A1.3.1 Nozzle - Stainless steel with a sharp, tapered edge. The tip diameter should be carefully measured. (Chemically inert material construction is permissible.)
Probe - Constructed to include an S-type pitot tube to measure stack gas velocity and a thermocouple to measure temperature. The liner should be chemically inert and be capable of being heated to 350?F (177?C). A Teflon liner may be used at stack gas temperatures lower than 500?F (260?C). Filter - The filter holder is constructed of inert material capable of supporting a glass fiber filter not less than four inches in diameter and capable of being heated to 350?F (177?C). Impingers - Impingers shall be standard and modified Greenburg-Smith designs or equivalent. They shall be connected by leak-free fittings. The first and third impingers are standard design; the second, fourth and fifth are modified. Method 8 Filter - The filter holder is constructed of glass or other inert material capable of supporting a two inch diameter or larger glass fiber filter. Gas Mover - A leak-free pump capable of moving at least one cubic foot per minute at 15" mercury vacuum; Metering System - The system shall. consist of a vacuum guage capable of mea.suring to 30" of mercury, a dry gas meter with an accuracy of ? 1% and thermometers or equivalent capable of measuring the temperatures of the inlet and outlet of the dry gas meter and the impinger outlet within 9?F (5?C). Sample Recovery Equipment -The equipment should include laboratory glassware, an analytical balance to measure f 0.1 mg, a balance to measure ? .1 gram, a pH meter and an atomic absorption spectrophotometer (AA) or other apparatus and procedures capable of measuring iron, copper, and zinc to 0.2 ppm and arsenic to 5.0 ppm. Filters - Glass fiber filters made without an organic binder and having a retention efficiency of 99.95% for 0.3 micron part1cles. Silica Gel - The silica gel shall be an indicating type, 6-16 mesh. If the silica gel has been used previously it should be dried at 350?F (177?C) for two hours. Water - The water should be deionized or distilled to conform to ASTM specification D 1193-72 Type 3.
Isopropanol 80% - This reagent is prepared by mixing 800 ml reagent grade isopropanol with 200 ml of deionized water. Thorin Indicator - This indicator solution is prepared by dissolving 0.2 g of 1-(0-arsonophenylazo)-2napthol-3, 6 disulfonic acid disodium salt in 100 ml of deionized or distilled water. Perchloric Acid 25% - This reagent is prepared by adding 25 ml of reagent grade perchloric acid (HCl04) to 75 ml of deionized or distilled water. Barim Perchlorate (O.OlN) - This titrant is prepared by d1ssolv1ng 1.95 g of barium perchlorate trihydrate (BaCl04. 3H2O) in 200 ml of deionized or distilled water and diluting to 1 liter with isopropanol. The pH of the solution is adjusted to 2.5-4.0 with 25% perchloric acid solution. It is then standardized with sulfuric acid of known concentration. Normal Sodium Hydroxide - An approximately one normal sodium hydroxide solution is prepared and standardized against a primary standard. Procedure Preparation All sampling train components shall be maintained and calibrated according to procedures described in APTD 0576, "Maintenance, Calibration, and Operation of Isokinetic Source Sampling Equipment", unless otherwise specified herein.
Check all filters visually against a light for irregularities and flaws or pinhole leaks. Label a glass fiber filter or its container and desiccate for at least twenty-four hours at 68. ? 10?F (20? ? 5.6?C) and ambient pressure. Weigh the filter or both the filter and container to the nearest 0.1 mg. If both the filter and container are weighed, the container must be weighed separately to determine the filter's exact weight. Carefully place filter in filter holder after weighing and seal the holder to prevent contamination. Weigh approximately 200 grams of silica gel to the nearest gram, place in the fifth impinger and seal. Place 200 ml of 80% isopropanol in the first impinger.
The second impinger is empty. Place 150 ml of 10% hydrogen peroxide in each of the third and fourth impingers. Weigh each of the five impingers to the nearest 0.1 g and record the weights. Seal probe, filter holder and all impingers to prevent contamination. Al.4.2 Preliminary Determinations Select the sampling site and the minimum number of sampling points according to EPA Method 1, 40 CFR 60, or as specified by the Director of ADEQ. Determine the stack pressure, temperature, and the range of velocity heads according to EPA Method 2, and moisture content according to Approximation Method 4 or its alternatives for the purpose of making isokinetic sampling rate calculations. Molecular weight of the carrier gas is determined by analyzing at least three "grab samples" with an Orsat analyzer during the sampling period. An alternative method may be approved by the Director. The samples are taken with a glass-wool packed tube extending far enough into the stack to get a representative sample. The gas samples are withdrawn from the stack with a one way aspirator bulb. The sampled gas is pumped into the Orsat apparatus and through the leveling fluid in the measuring burettes to saturate it with the gas to be analyzed. A1.4.2.l This Orsat apparatus is a commercially available instrument with three or more absorption burettes of the contact type. The apparatus is modified to analyze for sulfur dioxide, carbon dioxide, and oxygen. The sulfur dioxide absorbent is iodine-iodide solution that is made by dissolving 12.7 g of iodine and 83 g of potassium iodide in a liter of water. The carbon dioxide absorbent is aqueous 35% potassium hydroxide solution above. The oxygen absorbent is 5% pyrogallic acid in aqueous 35% potassium hydroxide. Gas absorbents which are commercially available may be substituted for the above. Leak check the apparatus by bringing the level in each absorption pipette up to the reference mark and closing the pipette stop-cock. In four minutes time the liquid level in the pipettes must not fall below the capillary. Adjust the level of the confining fluid
to the graduated portion ofthe measuring burette, lower the leveling bulb and take a reading. The level of the meniscus should not fall more than 0.2 ml in four minutes. A184.108.40.206 Draw the sample into the measuring burette after saturating the confining fluid with stack gas. Adjust to atmospheric pressure with a leveling bulb. Begin analysis by passing the sample gas several times through the sulfur dioxide absorbent. Take a reading, make one more pass and take another reading. Repeat the above procedure if necessary for a constant reading. Use the same procedure for carbon dioxide and for oxygen. This procedure assumes the carbon monoxide content of the gas to be negligible. The nitrogen percent is calculated by adding the percent of sulfur dioxide, carbon dioxide, and oxygen then subtracting from 100%. Calculate the dry molecular weight of the gas using the following formula: Md = 0.64(%S02) + 0.44(%CO2) + 0.32(%O2) + 0.28(%N 2) Estimates may be used for preliminary calculation of the isokinetic flow rate; however, final results will be calculated on actual measurements made by Orsat analyses during the test. A184.108.40.206 Select a nozzle size based on the range of velocity heads, such that it is not necessary to change the nozzle size in order to maintain isokinetic sampling rates. It is recommended that the nozzle size not be changed during sampling. Sample Site Preparation During preparation and assembly of the sampling train, keep all openings where contamination can occur covered until just prior to assembly or until sampling is about to begin. Mark the probe with heat resistant tape or by some other method to denote the sample traverse points as calculated by Method 1 during the preliminary determinations. A188.8.131.52 Set up the train as shown in Figure 1 using, if required, a very light coat of silicone grease on all ground glass joints, greasing only the outer portion to avoid the possibility of contamination by the silicone grease. (See APTD-0576.) After assembling the sample train at the test site,
seal the inlet to the filter holder, start the pump and carefully bring the vacuum to 15 inches of mercury. A leakage rate of 0.02 cfm or less is satisfactory. Close the coarse control valve and release the vacuum carefully before turning pump off to avoid transfer of impinger contents. Attach the probe, seal the inlet to the probe, and again leak check the system with a vacuum of 1 inch mercury using the above procedure. A188.8.131.52 Turn on probe and filter oven heaters and bring to a temperature of 325 ? 25?F (163 ? 15?C). During this period, add crushed ice to the impinger box and continue to add ice as needed after sampling has started to maintain the impinger gas at 70?F (21?C). Also clean the portholes prior to inserting the probe to avoid sample contamination with deposited material. Sampling When the temperatures of the probe and filter oven have reached the set point of 325?F (163?C), place the probe inlet at the first sampling point. When the probe is in position, block off the openings around the probe and porthole to prevent dilution of the gas stream. Begin sampling and record the required data as shown on the example sheet at least every five minutes. (See Figure 2.) Maintain sampling rate to within ten percent of isokinetic by adjusting the flow rate as necessary. Nomographs are avaliable for sampling trains using S-type pitot tubes with 0.85 ? 0.02 coefficient and when sampling stack gases of a molecular weight of 29 ? 4, which aid in the rapid adjustment of the sampling rate. A126.96.36.199 During the sampling, continue to check the probe and filter oven temperatures and the outlet temperature of the impingers. It is recommended that a leak check be conducted at each port change at the highest vacuum reading reached during that sampling traverse. If the pressure drop across the filter becomes too high to maintain an isokinetic sampling rate, the filter may be replaced during the run. It is recommended that a complete filter and filter, holder be used rather than changing the filter itself. A leak
check is then performed at 15 inches mercury as previously described. The particulate weight will include the summation of weight gains of all filters used in sampling. A126.96.36.199 After sampling has been completed and the minimum volume to provide a representative sample as specified by the Director has been reached, remove the probe from the flue, and record the dry gas meter reading. Again, leak check the system by plugging the inlet to the filter holder and pulling a vacuum equal to the highest vacuum recorded during the sample traverse. After the leak check, drain the icebath and begin purging the impingers by drawing clean ambient air through the inlet of the first impinger for approximately fifteen minutes at the sample rate. A charcoal filter may be used if necessary to ensure that clean air is being drawn. Sample Recovery Remove the sample train from the test site after the purge has been completed and the probe and filter oven have cooled. Insure that all probe, filter holder, and impinger openings are sealed to prevent contam1nat1on or loss of a sample dur1ng transit. A126.96.36.199 Disassemble the filter holder in a clean place. The filter holder and any glassware connecting the probe to the holder should be washed with 3:1 v/v acetone-heptane solution into a clean, dry container to collect the particulate. The filter also should be placed in this container. The probe and nozzle should be washed with the acetone-heptane solution using a nylon bristle brush into the container used for the filter. The container should be capped to prevent contamination. Typically, 100-200 ml of acetone-heptane mixture are used for particulate transfer. The impingers are weighed to determine the net weight gain of the sample train for the moisture content of the sampled gas. The weight of the sulfur dioxide collected is determined by titration (A126.96.36.199.) and subtracted from the weight gain (Equation 4) of the impingers before calculating the volume of water vapor collected. The first and second impingers are then rinsed into a clean container with water, along with
the wash of the Method a filter and filter holder. The Method a filter is transferred into the container. Any connecting glassware or tubing between the particulate filter holder and first impinger is also washed into the container. The third and fourth impingers and connectors are washed into a clean volumetric flask with deionized or distilled water. A1.4.6 Analysis Transfer the solutions from the first two impingers and Method a filter into a volumetric flask and dilute to the mark with deionized or distilled water. Pipette a 10 ml aliquot into a vessel for titration and evaporate on a hot plate to about 3 ml to remove any residual sulfur dioxide. Rinse the sides of the container with a minimum amount of water, cool, then add I isopropanol to make the solution 70-90% isopropanol. Add 2-4 drops of thorin indicator and titrate to the pink endpoint using 0.01 N barium perchlorate. Repeat, adjusting the size of the aliquots to obtain two accurate determinations. Prepare a blank by putting a same-size aliquot of distilled water through the above procedure. The blank and sample requiring 2.5 -3.0 ml titrant must be acidified with 1 to 2 drops of 25% perchloric acid before titration, so that the endpoint will be distinct. Save the contents of the volumetric flask for arsenic analysis by atomic absorption or other approved method. The arsenic determined is calculated as arsenous oxide and add to Mn used in equation Nos. 8 and 9 to calculate the total particulate concentration. A18.104.22.168 Dilute the contents of the volumetric flask containing the solutions from the peroxide impingers to the mark with deionized or distilled water. Withdraw a 10 to 25 ml aliquot and titrate to pH7 using standard sodium hydroxide. Repeat, adjusting the size of the aliquots to obtain two replicate determinations. A fine grade fiberglass filter (2.1cm) is placed in a Gooch crucible (Size No.3) seated in a crucible holder, which in turn is inserted into a filter flask. Vacuum is applied and deionized or distilled water is passed through the filter until it is well seated to
the crucible. Allow the excess water to be apirated. Dry the crucible in an oven at 105?C for at least 1 hour, cool in a dessicator, and weigh to the nearest 0.1 mg. A220.127.116.11 Break apart the particulates filter (in 3:1 acetoneheptane) into very fine pieces using the glass rods. Check that the filter in the pre-weighed Gooch filtration crucible is properly set. Using vacuum assist, filter and resulting slurry through the tared crucible using additonal anhydrous 3:1 acetone-heptane and a rubber policeman (or other means) to assure quantitative transfer. Rinse the contents of the crucible several times with 10 ml portions of 3:1 acetone-heptane. Dry the crucible for 3 hours at 105?C, cool in a dessicator, and weigh to the nearest 0.1 mg. The weight difference after subtracting the filter tare is the solid particulate weight. Transfer the filtrate from the above procedure to an appropriate container for evaporation of the acetoneheptane solvent. Also prepare a blank for analysis from 200 ml of 3:1 acetone-heptane. If a rotary evaporator is used, 50 ml of water is added and the organic solvent removed in a vacuum using a hot water bath. If a steam plate is used, the solvent is evaporated in a fume hood with occasional additions of water to avoid heating the sample to dryness. Evaporation of solvent on a hotplate in a fume hood is not recommended, however, it can be used if extreme care is exercised to avoid overheating and loss of sulfuric acid. Transfer the residual solution to 100 ml volumetric flask and make-up to mark with water. Titrate two 25 ml aliquots with 0.1 N sodium hydroxide to the phenolphthalein endpoint. Analyze the remainder of the solution and the solution from the first impingers for elements known to be present in the emissions in substantial quantities (as specified by the Director). Atomic absorption analysis in an air-acetylene flame or an equivalent method is acceptable. For AA analysis, background correction should be used or blanks and standards should be prepared in the proper sulfuric acid matrix. Blank values are subtracted from the determinations and the resulting concentrations are calculated as molecular
species likely to have been collected (as specified by the Director). The elemental contents are expressed as the hydrated sulfates and arsenic is expressed as arsenous oxide. (Fe2SO4 Y H2O. Zn2S04 Y CuSO4 and As2O3). Alternate equivalent methods of analysis may be approved by the Director. The weights of these compounds are added to (Mn) which is used in Equation Nos. 8 and 9 to calculate the particulate concentration.
AMBIENT TEMP., ?F__________________ BAR. PRESS., in HG_________________ ASSUMED MOISTURE, %________________ PROBE TIP DIAM., In._______________ STACK DIAM. (ft)___________________ STATICE PRESS. (in H 2O )____________ LEAK RATE @ ___ in H G __________cfm START/END TIME_____________________
SAMPLING TIME (0 min>)
GAS SAMPLE VOLUME (V M3 f t )
VELOCITY HEAD ( ? 3 in H2 0)
ORIFICE METER ( ? 3 in H2 0)
VACUUM (mHG)
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The Male Reproductive System
The internal organs of the male reproductive system, also called accessory organs, include the following:
Epididymis: The epididymis is a long, coiled tube that rests on the backside of each testicle. It transports and stores sperm cells that are produced in the testes. It also is the job of the epididymis to bring the sperm to maturity, since the sperm that emerge from the testes are immature and incapable of fertilization. During sexual arousal, contractions force the sperm into the vas deferens.
Vas deferens: The vas deferens is a long, muscular tube that travels from the epididymis into the pelvic cavity, to just behind the bladder. The vas deferens transports mature sperm to the urethra, the tube that carries urine or sperm to outside of the body, in preparation for ejaculation.
Ejaculatory ducts: These are formed by the fusion of the vas deferens and the seminal vesicles (see below). The ejaculatory ducts empty into the urethra.
Urethra: The urethra is the tube that carries urine from the bladder to outside of the body. In males, it has the additional function of ejaculating semen when the man reaches orgasm. When the penis is erect during sex, the flow of urine is blocked from the urethra, allowing only semen to be ejaculated at orgasm.
Seminal vesicles: The seminal vesicles are sac-like pouches that attach to the vas deferens near the base of the bladder. The seminal vesicles produce a sugar-rich fluid (fructose) that provides sperm with a source of energy to help them move. The fluid of the seminal vesicles makes up most of the volume of a man's ejaculatory fluid, or ejaculate.
Prostate gland: The prostate gland is a walnut-sized structure that is located below the urinary bladder in front of the rectum. The prostate gland contributes additional fluid to the ejaculate. Prostate fluids also help to nourish the sperm. The urethra, which carries the ejaculate to be expelled during orgasm, runs through the center of the prostate gland.
- Bulbourethral glands: Also called Cowper's glands, these are pea-sized structures located on the sides of the urethra just below the prostate gland. These glands produce a clear, slippery fluid that empties directly into the urethra. This fluid serves to lubricate the urethra and to neutralize any acidity that may be present due to residual drops of urine in the urethra.
How Does the Male Reproductive System Function?
The entire male reproductive system is dependent on hormones, which are chemicals that regulate the activity of many different types of cells or organs. The primary hormones involved in the male reproductive system are follicle-stimulating hormone, luteinizing hormone, and testosterone.
Follicle-stimulating hormone is necessary for sperm production (spermatogenesis), and luteinizing hormone stimulates the production of testosterone, which is also needed to make sperm. Testosterone is responsible for the development of male characteristics, including muscle mass and strength, fat distribution, bone mass, facial hair growth, voice change, and sex drive.
WebMD Medical Reference


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The Great American Race has come a long way since the pre-NASCAR days of racing on the sand and the A1A pavement of Daytona Beach. Since '59, the greatest racers in the world have assembled upon Daytona International Speedway for 500 miles of pure adrenaline. This year on February 26th, the field of 43 will give it their all for 200 laps and one racer will put their name in NASCAR's history books forever and celebrate in Victory Lane. Commemorate the rich tradition of racing in Daytona with this Daytona 500 canvas print. It features a large 54th Annual Daytona 500 logo printed on the canvas background which includes a historic print of the races on the sandy beaches on top and a print of the current Speedway at the bottom. It's a must have piece for any NASCAR fanatic.
- Canvas print
- Imported
- Measures approximately 11" x 14"
- Officially licensed Daytona 500 canvas
- Ready to hang (includes bracket)
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The Volvo A25F and A30F dumper are the hauler trucks depended on more jobsites around the globe. For dumper truck hauling in all terrain, from earthmoving and mining to material handling and waste handling, tunnelling and quarrying, Volvo has your solution.
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NASCAR is all about speed. It's where the world's best drivers compete for glory and for recognition. There is, however, only one driver who is the best of them all: Kevin Harvick. Kevin Harvick redefines speed in his #29 vehicle, and you should remind people of that in this Faster tee from Checkered Flag. Featuring the driver's number, vehicle and replica signature printed on the chest and his name printed down the left sleeve, this comfy shirt will let everyone know who's the fastest NASCAR driver there is!
- 90% Cotton/10% Polyester
- Imported
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- Screen print graphics
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Dear Members,
In order to show respect towards someones wishes, regarding if they want to get surprised by the new issue of the manga, please place the proper "Spoiler" prefix on your thread, whenever you create one that contains any spoilers. If you do decide to post any spoiler at all, while creating the thread, in the drop-down box before the thread title, again, please make sure you selected "Spoiler" as the thread prefix.
Thank you, NarutoBase Staff
why do Obito and Madara have that thing connected to the back of their neck
that link does not work
try now
It works the same like the Gedo does I think
Just sticking chakra Rods
Its the Gedo Mazo's wire it feeds them chakra
I think so when the jubbi attacks they wont fall off and for chakra
Using Juubi's chakra..
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What-cha think?
What-cha think?
Bow String Depot Custom String Builders
Need a string set pm or email me @ email@example.com
or check us out @ http://bowstringdepot.com
I can't really see the benefits of it for me. We can hunt 1/2 before, until 1/2 hour after sunset. It's still PLENTY light to shoot 1/2 hour after. Been many nights I have had ot sit in a stand to let deer move off that came in right after hunting hours. Could have shot dozens of them, but legal time is legal time. Not sure how many states allow hunting after sunset, but I think it would have to be pretty dark to need that peep, or lighted sights for that matter. Plus, it wouldn't do me any good to have all the lights in the world if I can't see the deer clearly. lol
2008 Moab 70# The deer killing bow
2008/12 Firecat 60#--- 2010 Warthog 70#
2009 Warthog 70#---2009-10-12? Warthog Frankenbow with Nitrous B
2010 Strother SR-71 65# & 2012 Strother Rush 65#
2012 Strother SX Rush 60# & 2011 Strother Infinity 70#
BSD strings and cables
Yeah, I know I'm grumpy and opinionated.
I'm not sold on it. Here in AZ you can hunt from dawn to dusk. The laws the law,,, and I would have to try the product to see if it may help right before dusk sitting in a blind and or in a tree stand with all the shadows. I wouldn't buy it to try it, but if they sent me one I give it a whirl and a review.
Ranger 6
2011 Fire Cat 400 (Custom)
2005 Martin SlayR
2012 Mathews z7 Magnum
2014 Mathews Creed
2001 PSE Excellerator
well iwant one. i get thirty min before sunrise and thirty after sunset for legal hours here in wi and that can be pretty dark on overcast days. maybe its only 20 min, the reg book gives you an exact time every day. only 11 bucks at bowhunters superstore! ordering one right now
thanks hutch
ps those strings are awesome. i'm now shootin a 9.5 gpi arrow like i used to shoot 7.3 gpi cx blue streaks, definitely going with the heavier arrows now!
Last edited by boobowbender; 07-25-2012 at 11:53 AM.
2011 Firecat 400, sword twilight hunter, apa twister, lots of arrows
ebay $11.39 FREE SHIPPING!
2011 Firecat 400, sword twilight hunter, apa twister, lots of arrows
Not sure I want to put anything that glows close to my eye when it gets dusk. Just might wash out anything in front of it. Besides, I have shot for so long that my form is down to a Tee and my bow tweaked likewise. When I draw a bow I don't need to see if the peep is in front of my eye. I know it is, therefore I see my pin through the hole. That pin and the intended target are all I wish to see.
I did notice in th video that he never stopped dropping his aim as he shot. Shooting on the move ain't good. Anticipate the shot and punch the trigger---no-no.
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What is the best way to remove serving or string nocking points without damaging the string? I know, very carefully!
What is the best way to remove serving or string nocking points without damaging the string? I know, very carefully!
Firecat 400
Bow String Depot Custom String Builders
Need a string set pm or email me @ firstname.lastname@example.com
or check us out @ http://bowstringdepot.com
Careful work with a single edge razor for me, too. I know that somebody just has to have some fancy gizmo to sell us to do the job, but old ways work just fine.
If You're Not Living on the Edge You're Taking Up Too Much Space
Martin Gold Plus Staff Shooter
Alien Mafia
PSAA Life member, UBP Life member
PADI AOW Diver
X3 on the razor blade for the serving. For the nockset, I use a pair of diagonal cutters VERY carefully. Just open it up enough to get something in to pry it open further with.
2008 Moab 70# The deer killing bow
2008/12 Firecat 60#--- 2010 Warthog 70#
2009 Warthog 70#---2009-10-12? Warthog Frankenbow with Nitrous B
2010 Strother SR-71 65# & 2012 Strother Rush 65#
2012 Strother SX Rush 60# & 2011 Strother Infinity 70#
BSD strings and cables
Yeah, I know I'm grumpy and opinionated.


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Huawei is a Global Fortune 500 company and one of the world's largest and fastest growing technologies solutions providers. With over 120,000 employees worldwide, Huawei is developing technologies used in 140 countries by one-third of the world's population. Huawei is leading the way by rethinking the future. From devices to telecom infrastructure to cloud computing and convergence solutions, we are rethinking every link in the chain with ICT based innovation to deliver a better future... faster.
Joining Huawei gives you the opportunity to become part of our explosive growth and help shape the future of telecommunications.
Welcome to Huawei Canada Careers Portal!
Search our positions by selecting a location below. To see all openings sorted by location select "-Any-". Alternatively, you can search our positions by job category. Hold the "Ctrl" key to highlight multiple job categories. Each job description includes a link for applying and submitting your resume to us online. This is the fastest and most reliable way to be considered for any of our positions.


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Contact details
Barley Cove Beach Holiday Homes are located right on the Golden Sandy Blue Flag Beach of Barley Cove on Mizen Head in West Cork. Ideal for families with full access to Barley Cove Beach Hotel (seasonal) with bar, restaurant, outdoor decking and magnificent sea views. Horse riding, golf and angling locally.
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Women's Health
Do Shopping Trips Help You Live Longer?
April 7, 2011 -- Regular trips to the store may help people live longer, even if they don't buy anything, according to researchers in Taiwan.
So does this mean "retail therapy" could be classed as an actual therapy for healthy aging? Other factors also come into play, one expert on aging tells WebMD.
Retail Therapy
The researchers in Taiwan say physical activity alongside social and economic activity are already recognized as being vital for healthy aging, but they say few studies have looked for a link between shopping and long-term survival.
Researchers in the U.K. looked at retail therapy in 2004 and concluded that rather than being a therapy in itself, shopping was a distraction from problems.
Researchers for the current study looked at 1,841 people aged 65 or over in Taiwan who lived independently at home. They were asked how often they went shopping. Possible answers ranged from "every day" to "never."
The answers were studied along with mental and physical capacities, age, gender, education, ethnicity, financial and employment status, lifestyle factors, and any long-term medical conditions. The study shows:
- 48% never shopped or shopped less than once per week.
- 22% shopped between two and four times a week.
- 17% shopped every day.
- The rest shopped once a week.
Sixty-two percent of the participants were younger than 75. Fifty-four percent were men, and 76% were financially self-sufficient.
Sixty percent had up to two long-term medical conditions.
Retail Results
Younger participants were more likely to shop more often. Contrary to the stereotype of the grumpy old man not wanting to be dragged to the store, men shopped more often than women did.
People who shopped more tended to be smokers and alcohol drinkers, but had better physical and mental health. They also took regular exercise and had a network of friends to have meals with.
When other factors were taken into account, daily shoppers were 27% less likely to die, with the men amongst them 28% less likely to die, compared with 23% of women.
What Does It Mean?
The authors admit that shopping could be linked to better health in the first place -- going to the store more often to stock up on fresh, healthy food, for example.
Visiting stores didn't need to end up with a new pair of shoes or another purchase. It could be more about a nice stroll with friends.
Writing in the Journal of Epidemiology and Community Health online, the authors say: "Shopping captures several dimensions of personal wellbeing, health and security, as well as contributing to the community's cohesiveness and economy, and may represent or actually confer increased longevity."
One of the authors, Mark Wahlqvist, MD, PhD, visiting professor at the National Health Research Institutes in Taiwan, tells WebMD by email, "It is of particular interest in that it provides apparent benefit for the less socio-economically advantaged (the poorer) and for men."
Compared to the West, he says there's a cultural difference, "which encourages both purposeful and recreational shopping -- along with the traditional Chinese love of buying and selling."
Today on WebMD
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Under Armour Holiday Classic
Torrey Pines High School hosted its 23rd annual boys prep Under Armour Holiday Classic Basketball Tournament presented by the Lucky Duck Foundation Dec. 26-29.
Tournaments were held in five divisions, with games played at various locations.
Teams from the United States and British Columbia, Canada were in attendance.
Visit www.theholidayclassic.org. Photos/Jon Clark
Related posts:
- Torrey Pines High School to host Under Armour Holiday Classic Basketball Tournament Dec. 26-29
- TPHS Holiday Prep Classic basketball tournament to be held Dec. 27-30
- Week in Sports: Falcons go 2-for-2 in holiday classic
- Holiday fun at Piazza Carmel
- Torrey Pines High School golfer wins Under Armour®/Hunter Mahan Championship
Short URL: http://www.delmartimes.net/?p=44114
Posted by Staff on Jan 4, 2013. Filed under Featured Story. You can follow any responses to this entry through the RSS 2.0. You can leave a response or trackback to this entry


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If there is anything short people want the most is increasing their height. If you have been to any firm, you have probably noticed that most of the senior management is made up of tall people. This is mainly due to the attributes that come with being tall. Tall people are known to have a voice that can command others easily; they are authoritative and are generally seen as a symbol of power. Employees are known to be able to heed to directions given by tall people than those given by shorter people. Shorter people on the other hand are left wondering on what they should do in order for them to be able to size up and be able to have a voice just like the taller people.
One of the best ways on how to grow taller for idiots is doing plenty of exercises. Exercising has many advantages on the body thus if you want to really size up, you must be able to exercise more often. Through exercises, you are able to stretch the body and the backbone plates thus you are able to increase your height. In the past, there are many people who have managed to grow taller after doing exercises. A good example is the athletes. When you look at most athletes, you will notice that they are taller than the average person. Next time, consider working out regularly and often and you should be shocked on how tall you may grow.
If you are that kind of a person who doesn't have a diet plan, then you should consider getting yourself a diet plan. People without diet plans don't know what they really supply the body with and they are more likely to experience a lot of challenges. When it comes to growing taller, there is need to know what kind of foods you are taking and the impact they can have on your body. You can seek the help of nutritionist to help you come up with a diet plan that can help you grow taller.
Sleep is yet another important aspect that you must consider if you want to grow taller. Sleeping for the required amounts of time will go a long way into helping you grow taller for idiots. Basically, it is during sleep that your body is able to release the growth hormones. Your body is also able to repair any damaged tissues and replenish energy that was spent during the day.


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Knight Internship Fellowship Recipient 2009
My time at the Mutter museum has been fantastic. I spent my summer assisting the exhibitions coordinator in constructing a new space within an old gallery. I became familiar with the fabrication of walls, inset cases and archival processes therein. I enjoyed the physicality of the revitalization process.
On days when I was free to draw, study the body, sketch in the medicinal garden and research in the library, I spent time doing research for my thesis. I plan to focus much of the current semester on the sensory context of the body. This experience has been helpful for the direction of my thesis and to expand my career options.
My experience at the Mutter has been excitingly varied and intellectually stimulating.
Read more about The Knight Internship
Read about the Mutter Museum
Janelle Adamski
Knight Internship Fellowship Recipient 2009