Practical Guide EDEXCEL

Total Page:16

File Type:pdf, Size:1020Kb

Practical Guide EDEXCEL Practical Guide EDEXCEL This guide includes details about the core practicals for A-level chemistry. It also contains information about other experiments that often occur in A-level examinations. You may be asked to describe these experiments in details or be asked about reasons for doing individual steps. You may be asked about other unfamiliar experiments but these will be using the skills and techniques that are described in the following experiments. Safety and hazards Irritant - dilute acid and alkalis- wear googles Hazardous substances in low Corrosive- stronger acids and alkalis wear goggles concentrations or amounts will Flammable – keep away from naked flames not pose the same risks as the Toxic – wear gloves- avoid skin contact- wash hands after use pure substance. Oxidising- Keep away from flammable / easily oxidised materials Measuring gas volumes Make sure you don’t leave gaps in Using a gas syringe your diagram where gas could Gas syringes can be used for a variety of escape experiments where the volume of a gas is measured, possibly to work out moles of gas or to follow reaction rates. Potential errors in using a gas syringe •gas escapes before bung inserted If drawing a gas syringe make sure •syringe sticks you draw it with some • some gases like carbon dioxide or sulphur dioxide are measurement markings on the soluble in water so the true amount of gas is not barrel to show measurements can measured. be made. The volume of a gas depends on pressure Alternatively gas volumes can be and temperature so when recording volume measured ‘over water’ with an up-turned it is important to note down the measuring cylinder in a trough of water temperature and pressure of the room. Moles of gas can be calculated from gas volume (and temperature and pressure) using ideal gas equation PV = nRT or using the molar gas volume (1mol gas =24dm3 at room temperature and pressure N Goalby chemrevise.org 1 Core Practical 1: Measure the molar volume of a gas Detailed method 1. Measure 30 cm3 of 1 mol dm 3 ethanoic acid and transfer to a conical flask. 2. Attach conical flask to gas syringe⁻ or use collection over 3 water method (see previous page) in cmin 3. Measure the mass of a weighing bottle with approximately 2 0.05 g of calcium carbonate 4. Add the calcium carbonate to the conical flask- quickly resealing the bung so no gas escapes 5. Measure the final total volume of gas 6. Reweigh the empty weighing bottle test tube from step 3 CO of Volume 7. Repeat the experiment several more times, increasing the mass of calcium carbonate by about 0.05 g each time. Mass of CaCO3 in g Analysis From the graph read the volume of CO2 given off with 0.25 g CaCO3 -3 Work out the moles of CaCO3 in 0.25g = 0.25/100.1 = 2.5 x 10 Assume the moles of CO2 = moles of CaCO3 Work out molar volume of CO2 = volume of CO2/ moles of CO2 Method for using a gas syringe to calculate the Mr of propanone 1. Extract 0.20 cm3 of propanone into a hypodermic syringe and then measure the mass of this syringe 2. using hand protection, remove a gas syringe from the oven and note the volume of air already in the barrel – about 5 cm3. 3. inject the propanone through the self-seal cap into the barrel. The plunger will move straight away. 4. Put the gas syringe back into the oven. 5. Measure the mass of the empty hypodermic syringe immediately. 6. After a few minutes measure the volume of the gas in the gas syringe, record the temperature of the oven shelf and the pressure of the room. Example 1 : 0.150g of a volatile liquid was injected into a sealed gas syringe. The gas syringe was placed in an oven at 70oC at a pressure of 100kPa and a volume of 80cm3 was measured. Calculate the Mr of the volatile liquid (R = 8.31) moles = PV/RT 100 kPa = 100 000 Pa = 100 000 x 0.00008 / (8.31 x 343) 80 cm3 = 0.00008 m3 = 0.00281 mol Mr = mass/moles = 0.15 / 0.00281 = 53.4 g mol-1 N Goalby chemrevise.org 2 Heating in a crucible This method could be used for measuring mass loss in various thermal decomposition reactions and also for mass gain when reacting magnesium in oxygen. The water of crystallisation in calcium sulfate crystals can be The lid improves the accuracy of the removed as water vapour by heating as shown in the following experiment as it prevents loss of solid equation. from the crucible but should be loose CaSO4.xH2O(s) → CaSO4(s) + xH2O(g) fitting to allow gas to escape. Method. •Weigh an empty clean dry crucible and lid . •Add 2g of hydrated calcium sulphate to the crucible and weigh again •Heat strongly with a Bunsen for a couple of minutes •Allow to cool •Weigh the crucible and contents again •Heat crucible again and reweigh until you reach a constant mass ( do this to ensure reaction is complete). Large amounts of hydrated calcium sulfate, such as 50g, should not be used in this experiment as the decomposition is likely to be incomplete. Small amounts of the solid , such as 0.100 g, should not be used in this The crucible needs to be dry otherwise a wet crucible would experiment as the percentage give an inaccurate result. It would cause mass loss to be too uncertainties in weighing will be too large as the water would be lost when heating. high. Example 2. 3.51 g of hydrated zinc sulfate were heated and 1.97 g of anhydrous zinc sulfate were obtained. Use these data to calculate the value of the integer x in ZnSO4.xH2O Calculate the mass of H2O = 3.51 – 1.97 = 1.54g Calculate moles of 1.97 Calculate moles of = 1.54 = H O ZnSO4 161.5 2 18 = 0.0122 =0.085 Calculate ratio of mole of = 0.0122 = 0.085 ZnSO4 to H2O 0.0122 0.0122 =7 =1 X = 7 N Goalby chemrevise.org 3 Core practical 2. Make up a volumetric solution and carry out a simple acid–base titration Making a solution • Weigh the sample bottle containing the required mass of solid Alternatively the known mass of solid on a 2 dp balance in the weighing bottle could be • Transfer to beaker transferred to beaker, washed and • Reweigh empty sample bottle washings added to the beaker. • Record the difference in mass • Add 100cm3 of distilled water to the beaker. Use a glass rod to stir to help dissolve the solid. •Sometimes the substance may not dissolve well in cold water so the beaker and its contents could be heated gently until all the solid had dissolved. Remember to fill so the bottom of the • Pour solution into a 250cm3 graduated flask via a funnel. meniscus sits on the line on the neck of the • Rinse beaker and funnel and add washings from the beaker flask. With dark liquids like potassium and glass rod to the volumetric flask. manganate it can be difficult to see the • make up to the mark with distilled water using a dropping meniscus. pipette for last few drops. • Invert flask several times to ensure uniform solution. Shake the volumetric flask thoroughly to ensure a uniform concentration A graduated flask has one mark on the neck which the level to fill to get the accurate volume. Do not heat or put hot solutions in the volumetric flask because the heat would cause the flask to expand and the volume would then be incorrect. Measuring mass accurately: In many experiments the best method for measuring mass is 1. Measure mass on 2 or 3d.p. balance of a weighing bottle with the required quantity of solid in it 2. Empty mass into reaction vessel/flask 3. Reweigh the now empty weighing bottle 4. Subtract the mass of the empty weighing bottle from the Graduated/volumetric flask first reading to give exact of mass actually added. Dilutions Diluting a solution Using a volumetric pipette is more accurate than a measuring cylinder because it has a 3 3 •Pipette 25cm of original solution into a 250cm volumetric smaller uncertainty flask •make up to the mark with distilled water using a dropping Use a teat pipette to make up to the mark in pipette for last few drops. volumetric flask to ensure volume of solution • Invert flask several times to ensure uniform solution. accurately measured and one doesn’t go over the line N Goalby chemrevise.org 4 Titrations Core Practical 3: Make up a volumetric solution and carry out a simple acid–base titration General Method •rinse equipment (burette with acid, pipette with alkali, conical flask with distilled water) •pipette 25 cm3 of alkali into conical flask •touch surface of alkali with pipette ( to ensure correct amount is added) •adds acid solution from burette •make sure the jet space in the burette is filled with acid •add a few drops of indicator and refer to colour change at end point •phenolphthalein [pink (alkali) to colourless (acid): end point pink colour just disappears] [use if NaOH is used] •methyl orange [yellow (alkali) to red (acid): end point orange] [use if HCl is used] •use a white tile underneath the flask to help observe the colour change •add acid to alkali whilst swirling the mixture and add acid drop wise at end point •note burette reading before and after addition of acid •repeats titration until at least 2 concordant results are obtained- two readings within 0.1 of each other Titrations are done often to find out the concentration of one substance by reacting it with another substance of known concentration.
Recommended publications
  • Standard Operating Procedure SEA05 Laboratory Analysis-Version
    Gulf Coast Network National Park Service Inventory and Monitoring Division Standard Operating Procedure SEA05 Laboratory Analysis—Version 1.0 Please cite this as: Meiman, J. 2019. Laboratory Analysis—Version 1.0. Gulf Coast Network Standard Operating Procedure NPS/GULN/SOP—SEA05. Gulf Coast Network, Lafayette, Louisiana. Summary This standard operating procedure (SOP) for laboratory analysis of total suspended solids (TSS) is adopted verbatim from USEPA Method 160.2. Revision Log Revision Date Author Changes Made Reason for Change New Version # METHOD #: 160.2 Approved for NPDES (Issued 1971) TITLE: Residue, Non-Filterable (Gravimetric, Dried at 103–105°C) ANALYTE: Residue, Non-Filterable INSTRUMENTATION: Drying Oven STORET No. 00530 1. Scope and Application a. This method is applicable to drinking, surface, and saline waters, domestic and industrial wastes. b. The practical range of the determination is 4 mg / L to 20,000 mg / L. 2. Summary of Method a. A well-mixed sample is filtered through a glass fiber filter, and the residue retained on the filter is dried to constant weight at 103-105°C. b. The filtrate from this method may be used for Residue, Filterable. 3. Definitions a. Residue, non-filterable, is defined as those solids which are retained by a glass fiber filter and dried to constant weight at 103-105°C. 4. Sample Handling and Preservation a. Non-representative particulates such as leaves, sticks, fish, and lumps of fecal matter should be excluded from the sample if it is determined that their inclusion is not desired in the final result. b. Preservation of the sample is not practical; analysis should begin as soon as possible.
    [Show full text]
  • SILICA, CRYSTALLINE in Coal Mine Dust, by IR 7603
    SILICA, CRYSTALLINE in coal mine dust, by IR 7603 SiO2 MW: 60.08 CAS: 14808-60-7 RTECS: VV7330000 METHOD: 7603, Issue 2 EVALUATION: UNRATED Issue 1: 15 May 1989 Issue 2: 15 August 1994 quartz (respirable): 3 OSHA : 10 mg/m /(%SiO2 + 2) PROPERTIES: solid; crystalline transformations: quartz NIOSH: 0.05 mg/m3 (suspect carcinogen) to tridymite @ 867 °C: tridymite to ACGIH: 0.1 mg/m3 crystobalite @ 1470 °C; a-quartz to b-quartz @ 573 °C SYNONYMS: free crystalline silica; silicon dioxide SAMPLING MEASUREMENT SAMPLER: CYCLONE + PREWEIGHED FILTER TECHNIQUE: INFRARED SPECTROPHOTOMETRY (IR) (10-mm cyclone, nylon, or Higgins-Dewell (HD), and PVC filter, 37-mm, 5-µm) ANALYTE: quartz FLOW RATE: HD cyclone: 2.2 L/min WEIGH: dust cassette nylon cyclone: 1.7 L/min ASH: muffle furnace or RF plasma asher VOL-MIN: 300 L @ 0.1 mg/m 3 -MAX: 1000 L REDEPOSIT: 0.45-µm acrylic copolymer membrane filter SHIPMENT: routine IR: scan, 1000 to 650 cm -1, absorbance mode SAMPLE STABILITY: stable with blank filter in reference beam BLANKS: 2 to 10 field blanks per set CALIBRATION: standard suspension of quartz in 2-propanol BULK SAMPLE: required for OSHA standard calculations; area respirable or settled dust RANGE: 30 to 250 µg quartz per sample [1] ESTIMATED LOD: 10 µg quartz per sample [1] ACCURACY PRECISION (S r): 0.098 @ 100 to 500 µg per sample RANGE STUDIED: 25 to 160 µg/sample [1] (varies with sample matrix) [1] (2 mg quartz/m 3 atmosphere) BIAS: unknown ˆ OVERALL PRECISION (S rT): 0.13 to 0.22 (varies with sample loading and matrix) ACCURACY: ±25.6 to 43.4% APPLICABILITY: The working range is 0.03 to 2 mg/m 3 for a 1000-L sample.
    [Show full text]
  • SILICA, CRYSTALLINE, by XRD (Filter Redeposition) 7500
    SILICA, CRYSTALLINE, by XRD (filter redeposition) 7500 SiO2 MW: 60.08 CAS: 14808-60-7 (quartz) RTECS: VV7330000 (quartz) 14464-46-1 (cristobalite) VV7325000 (cristobalite) 15468-32-3 (tridymite) VV7335000 (tridymite) METHOD: 7500, Issue 4 EVALUATION: FULL Issue 1: 15 August 1990 Issue 4: 15 March 2003 3 3 OSHA : quartz (respirable) 10 mg/m /(%SiO2+2); PROPERTIES: solid; d 2.65 g/cm @ 0 °C; crystalline cristobalite and tridymite (respirable) ½ the above transformations: quartz to tridymite NIOSH: 0.05 mg/m3; carcinogen @ 867 °C; tridymite to cristobalite ACGIH: quartz (respirable) 0.1 mg/m3 @ 1470 °C; "-quartz to ß-quartz cristobalite (respirable) 0.05 mg/m3 @ 573 °C tridymite (respirable) 0.05 mg/m3 SYNONYMS: free crystalline silica; silicon dioxide SAMPLING MEASUREMENT SAMPLER: CYCLONE + FILTER TECHNIQUE: X-RAY POWDER DIFFRACTION (10-mm nylon cyclone, Higgins- Dewell (HD) cyclone, or aluminum ANALYTE: Crystalline SiO2 cyclone + 5-:m PVC membrane) *see sampling section ASH: Muffle furnace or RF plasma asher or dissolve in tetrahydrofuran FLOW RATE: Nylon cyclone: 1.7 L/min; HD cyclone: 2.2 L/min; REDEPOSIT: On 0.45-:m Ag membrane filter aluminum cyclone: 2.5 L/min XRD: Cu target X-ray tube, graphite VOL-MIN: 400 L monochromator -MAX: 1000 L Optimize for intensity; 1° slit Slow step scan, 0.02°/10 sec SHIPMENT: Routine Integrated intensity with background subtraction SAMPLE STABILITY: Stable CALIBRATION: :NIST SRM 1878a quartz, NIST SRM 1879a cristobalite, USGS 210-75-0043 BLANKS: 2 to 10 per set (see step 13.g.) tridymite suspensions in 2-propanol. BULK SAMPLE: High-volume or settled dust; to RANGE: 0.02 to 2 mg SiO2 per sample [2] identify interferences ESTIMATED LOD: 0.005 mg SiO2 per sample [2] ACCURACY þ PRECISION ( r): 0.08 @ 0.05 to 0.2 mg per sample [1] RANGE STUDIED: 25 to 2500 :g/m3 [1] (800-L sample) BIAS: None known Ö : OVERALL PRECISION ( rT): 0.09 (50 to 200 g) [1] ACCURACY: ± 18% APPLICABILITY: The working range is 0.025 to 2.5 mg/m3 for an 800-L air sample.
    [Show full text]
  • Edna PROTOCOL SAMPLE COLLECTION
    eDNA PROTOCOL SAMPLE COLLECTION Caren Goldberg and Katherine Strickler, Washington State University September 2014 Adapted from Protocol Version 04/12/2012 (D.S. Pilliod, R.S. Arkle, and M.B. Laramie) USGS Snake River Field Station MATERIALS 1. Cellulose nitrate disposable filter funnels or other field-tested, disposable filter funnels 2. Vacuum flask (1L) 3. Silicone tubing 4. Vacuum hand pump (from auto parts store) 5. Rubber stopper with hole for funnel stem 6. Latex or nitrile gloves (non-powdered) 7. Forceps (filter forceps if possible) 8. High quality, o-ring screw cap 2mL tubes (e.g., Sarstedt brand) with 1mL 100% molecular-grade ethanol (not denatured) 9. Ethanol-proof laboratory pen (do not use a regular Sharpie marker) 10. 50 mL tubes of 30 mL 1) 50% household bleach solution 2) distilled water in a holder (a foam drink holder [koozie] works well) 11. Polypropylene grab bottles and cooler (for off-site filtering) or Whirl-Pak® bags (for on- site filtering) 12. Water, bleach, scrub brush, and tubs (for decontaminating between sites) 2 3 5 1 4 2 Figure 1. Filter funnel (1), vacuum flask (2), silicone tubing (3), vacuum pump (4), and rubber stopper (5). 9 7 10 8 6 1 Figure 2. Latex or nitrile gloves (6), forceps (7), 2 mL tubes with 1 mL ethanol (8), ethanol-proof lab marker (9), and 2 50 mL tubes with 50% household bleach solution distilled water (10). 3 11a 11b Figure 3. Polypropylene grab bottles (11a) and Whirl-Pak® bag (11b). 12a 12d 12b 12c Figure 4. Water (12a), bleach (12b), scrub brushes (12c), and tubs (12d) for decontaminating boots and equipment between sites.
    [Show full text]
  • Laboratory Filtration Principles and Chemical Compatibility Chart Filtration Simplified
    Laboratory filtration Principles and chemical compatibility chart Filtration simplified Basic filtration concepts and terms Selecting a filter with the appropriate properties can help you achieve accurate results and reach discovery faster. But with so many types of filters to choose from, how can you be sure you’re making the right choice? GE Healthcare Life Sciences, maker of Whatman™ brand filtration products, has assembled this compilation of basic filtration concepts and terms to clarify the various options available to you and speed up your selection process. Ash content Hydrophilic Determined by ignition of the cellulose filter at 900°C Because hydrophilic filters possess an affinity for water in air. Minimizing ash content is essential in gravimetric and can be wetted with virtually any liquid, they are applications and also a useful measure of the level of typically used for aqueous solutions and compatible general purity. organic solvents. Chemical compatibility Hydrophobic It is very important to ensure that the structure of the These types of filters repel water, and are thus best suited filter media will not be impaired by exposure to certain for filtering organic solvents as well as for venting and chemicals. In addition, exposure to these chemicals gas filtration applications. should not cause the filter to shed fibers or particles, or add extractables. Length of exposure time, temperature, Liquid flow rate (including Herzberg method) concentration and applied pressure can all affect Under practical filtration conditions, the liquid flow rate compatibility. GE Healthcare has provided chemical will depend on a number of factors, many of which will compatibility charts to aid your filter selection.
    [Show full text]
  • Environmental DNA Sampling Protocol—Filtering Water to Capture DNA from Aquatic Organisms
    Prepared in cooperation with Washington State University Environmental DNA Sampling Protocol—Filtering Water to Capture DNA from Aquatic Organisms Chapter 13 of Section A, Biological Science Book 2, Collection of Environmental Data Techniques and Methods 2–A13 U.S. Department of the Interior U.S. Geological Survey Cover: Okanogan River, British Columbia, Canada, 2012. Insets from top to bottom: Juvenile rainbow trout from Ratz Creek, Alaska, 2009. (C)2009 ADF&G, Division of Sport Fish. Used with permission. Collecting eDNA sample from Boise River, Boise, Idaho, 2011. USGS Technician Kevin Glueckert collects eDNA sample from Boise River, Boise, Idaho, 2014. Preserving folded eDNA sample in ethanol vial-filled vial, 2012. Photographs by Matthew B. Laramie, U.S. Geological Survey, unless otherwise noted. Environmental DNA Sampling Protocol— Filtering Water to Capture DNA from Aquatic Organisms By Matthew B. Laramie, David S. Pilliod, Caren S. Goldberg, and Katherine M. Strickler Chapter 13 of Section A, Biological Science Book 2, Collection of Environmental Data Prepared in cooperation with Washington State University Techniques and Methods 2–A13 U.S. Department of the Interior U.S. Geological Survey U.S. Department of the Interior SALLY JEWELL, Secretary U.S. Geological Survey Suzette M. Kimball, Acting Director U.S. Geological Survey, Reston, Virginia: 2015 For more information on the USGS—the Federal source for science about the Earth, its natural and living resources, natural hazards, and the environment—visit http://www.usgs.gov or call 1–888–ASK–USGS. For an overview of USGS information products, including maps, imagery, and publications, visit http://www.usgs.gov/pubprod/.
    [Show full text]
  • Chemistry Lab Kit Instructions
    CHEMISTRY LAB KIT INSTRUCTIONS Not suitable for children under 10 years. For use under WARNING! adult supervision. Contains some chemicals which present a hazard to health. Read the instructions before use, follow them and keep them for reference. Do not allow chemicals to come into contact with any part of the body, particularly mouth and eyes. Keep small children and animals away from experiments. Keep the experimental set out of reach of children under 10 years old. Eye protection for supervising adults is not included. MADE IN CHINA P38-CM001-81001003 CONTENTS : 2 Test Tubes with Stoppers 1 Cleaning Brush 1 Test Tube Holder 2 Glass Tubing 1 Rubber Tubing 1 Spirit Lamp 1 Beaker(0-100ml) 1 Stirring Rod 1 Measuring Spoon 6 Filter Papers 8 Universal Indicator Paper 1 Goggles 2 Cork Stoppers with hole 1 Funnel 2 Cork Stoppers 1 Instruction Book 1 Scoop 1 Dropping Pipette 1 Test Tube Rack The Safety Rules Read these instructions before use, follow them and keep them for reference. Keep young children, animals and those not wearing eye protection away from the experimental area. Always wear eye protection. Store this experimental set out of reach of children under 10 years of age. Clean all equipment after use. Make sure that all containers are fully closed and properly stored after use. Ensure that all empty containers are disposed of properly; Wash hands after carrying out experiments. DO NOT use any equipment which has not been supplied with the set or recommended in the instructions for use. DO NOT eat or drink in the experimental area.
    [Show full text]
  • Recrystallization and Identification of an Unknown Solid
    Experiment 1: Recrystallization and Identification of an Unknown Solid I. Recrystallization Procedure: You will be given an unknown solid compound to purify by recrystallization using water as the recrystallizing solvent. The unknown will either be benzamide or 2- ethoxybenzamide and will contain a water-soluble organic impurity and a black carbon insoluble impurity. Note that the melting point ranges of benzamide and 2- ethoxybenzamide are quite close, so good technique will be required to distinguish between them. O O NH NH2 2 OCH2CH3 benzamide 2-ethoxybenzamide Pertinent information about the chemicals you are using: Reagents MW (g/mol) MP (ºC) BP (ºC) Density Benzamide 128-130 2-ethoxybenzamide 132-134 Water 18 0 100 1 Throughout this experiment, clean all glassware and equipment before using it. To clean it, wash with soap and water, rinse with water, and shake as much water as possible from it. If soap and water does not completely clean it (i.e. there is still some visible residue in it), wash with a little acetone then with water. The residue is likely organic material that the acetone will remove. This cleaning technique can be used in this experiment because water is being used as the solvent; a trace of water in the glassware will do no harm. Recrystallization of a Solid Compound: Dissolving the Solid: 1. Place a clean 250-mL Erlenmeyer flask containing approximately 100-mL water and 3- 4 boiling stones on a hot plate set to about 6; this will be used as your source of hot water when dissolving your compound for the experiment.
    [Show full text]
  • Volumetric Flask
    Chemical Analysis Solution (Consumables) Nobel Laboratory Sdn. Bhd. Contents Beaker ............................................ pg. 01 Flask ............................................ pg. 02 Disk ............................................ pg. 05 Tube ............................................ pg. 07 Bottle ............................................ pg. 09 Funnel ............................................ pg. 11 Measure ............................................ pg. 13 Plastic Product ............................................ pg. 17 Rubber Product ............................................ pg. 27 Metalwares ............................................ pg. 31 Laboratory Accessories ............................................ pg. 34 Glassware Our glassware are made of high quality borosilicate glass, with competitive price and good quality. Beaker Low Type Beaker Description Specication Low Type Beaker 5-10000ml High Type Beaker Description Specication High Type Beaker 50-2000ml Conical Beaker Description Specication Conical Beaker 125-800ml Beaker with Handle Description Specication Beaker with Handle 100-1000ml 01 Flask Flat Bottom Flask Description Specication Flat Bottom Flask 5-20000ml Flat Bottom Flask (Ground Neck) 100-1000ml, Joint 14, 19, 24, 29, 40, 50 Round Bottom Flask Description Specication Round Bottom Flask 5-20000ml Round Bottom Flask (Ground Neck) 10-10000ml, Joint 14, 19, 24, 29, 40, 50 Kjeldahl Flask Description Specication Kjeldahl Flask 250-1000ml 02 Conical / Erlenmeyer Flask Description Specication
    [Show full text]
  • Membrane Filtration (Simultaneous Detection) for Detection Of: Total Coliforms, E
    EPA Approved* Method 10029 Coliforms: Membrane Filtration (simultaneous detection) For detection of: total coliforms, E. coli Media: m-ColiBlue24® Broth Sample Type: potable water, nonpotable water, wastewater Simultaneous Total Coliform and E. coli Screening Hach’s new m-ColiBlue24®** Broth allows for the simultaneous detection of total coliform bacteria and Escherichia coli (E. coli) within 24 hours. An enzymatic indicator in the medium causes non-fecal total coliform colonies grown on the m-ColiBlue24 medium to be red, while the E. coli (fecal coliform) colonies are blue. The selectivity of the enzymatic indicator eliminates the need for confirmation. The low false positive and false negative rates allow for the detection of at least 95% of all E. coli. m-ColiBlue24 Broth enhances the growth rate of coliform bacteria and optimizes the recovery of stressed or injured organisms. Special inhibitors in the medium efficiently minimize the growth of non-coliform bacteria. Convenient Packaging Hach’s m-ColiBlue24 Broth comes in ready-to-use PourRite™ Ampules; no need to measure, mix, or autoclave. The ampules have a large, unrestrictive opening that allows the medium to pour easily. Simply break the top off the ampule, using the Hach ampule breaker, and pour the medium onto an absorbent pad in a petri dish. Each ampule contains enough selective medium for one test. Medium in PourRite ampules has a shelf life of one year. Ampules are shipped with a Certificate of Analysis and have an expiration date printed on the label. m-ColiBlue24 Broth is also available in plastic ampules and 100 mL bottles. Specifications Incubation: 24 hours at 35 ± 0.5 °C Sensitivity: 1 CFU/100 mL Selectivity: Detects total coliforms and E.
    [Show full text]
  • Experiment 5
    Experiment Aspirin Synthesis 5 Aspirin is the common name for the compound acetylsalicylic acid, widely used as a fever reducer and as a pain killer. Salicylic acid, whose name comes from Salix, the willow family of plants, was derived from willow bark extracts. In folk medicine, willow bark teas were used as headache remedies and other tonics. Nowadays, salicylic acid is administered in the form of aspirin which is less irritating to the stomach than salicylic acid. To prepare aspirin, salicylic acid is reacted with an excess of acetic anhydride. A small amount of a strong acid is used as a catalyst which speeds up the reaction. In this experiment, phosphoric acid will be used as the catalyst. The excess acetic acid will be quenched with the addition of water. The aspirin product is not very soluble in water so the aspirin product will precipitate when water is added. The synthesis reaction of aspirin is shown below: H3PO4 102 g/ mol 138 g/mol d = 1.08 g/mL 180 g/mol Since acetic acid is very soluble in water, it is easily separated from the aspirin product. The aspirin isolated in this step is the “crude product”. A “purified product” can be obtained through recrystallization of the crude product in hot ethanol. In this experiment, the crude product will be the desired product. The percent yield of the crude product will be determined for this reaction. The purity of the product will also be analyzed. The product will be analyzed by three different methods: melting point, titration, and spectroscopic assay.
    [Show full text]
  • Released Or Absorbed) During a Chemical Reaction
    DAT GENERAL CHEMISTRY LAB INFORMATION Basic Techniques Calorimetry Calorimetry is used to measure the change in heat (released or absorbed) during a chemical reaction. In chemistry labs, the setup for calorimetry generally consists of a Styrofoam cup with a sealed lid and hole for thermometer to measure the change in temperature during the reaction. Centrifugation Centrifugation is used to separate solids and liquids in heterogeneous mixtures. Successful separation results in the solid portion (pellet) at the bottom of the centrifuge tube and the liquid portion (supernatant) above it. When using a centrifuge, it is important that it remains balanced at all times – any tube being spun should have one of equal volume placed in the opposite slot. Quantitative Transfer Proper quantitative transfer methods ensure that the entire quantity of a substance has been transferred (for example, if an experiment requires that 5g of a powder are transferred into a beaker, it is easy for small amounts of the powder to be lost during transfer or left behind on the transfer medium – this can affect accuracy of results). When transferring powders, the mass should first be measured on creased weighing paper. Next, the weighing paper should carefully be folded and tipped into its destination (e.g. a beaker). A spatula should then be tapped against the paper to dislodge any remaining powder. Finally, the paper should be rinsed into the beaker to ensure full transfer of the powder. When transferring a liquid, after it is poured into its destination, the sides of the vessel it was poured from should be rinsed with solvent and continue to be poured into the destination to ensure that all of the liquid has been transferred.
    [Show full text]