LABORATORY ANALYSIS OF CATALYTIC CONVERTERS LEADS TO BETTER ENFORCEMENT RESULTS



Similar documents
UNITED STATES CONSUMER PRODUCT SAFETY COMMISSION DIRECTORATE FOR LABORATORY SCIENCES DIVISION OF CHEMISTRY 5 RESEARCH PLACE ROCKVILLE, MD 20850

Balancing chemical reaction equations (stoichiometry)

Pollution by 2-Stroke Engines

Austin Peay State University Department of Chemistry CHEM Empirical Formula of a Compound

IB Chemistry. DP Chemistry Review

EDXRF of Used Automotive Catalytic Converters

Determination of the enthalpy of combustion using a bomb calorimeter TEC. Safety precautions

VW 2-liter diesel car denial of recall, and Notice of Violation. Frequently Asked Questions:

Data Mining Tools. Sorted Displays Histograms SIeve

AUTOMOTIVE GAS OIL. Robert Shisoka Hydrocarbon Management Consultancy

For Discussion Purposes Only. Direct Metals Recycling Financing Opportunity. (Note: All figures contained herein are in US dollars)

The Empirical Formula of a Compound

Determination of the enthalpy of combustion using a bomb calorimeter TEC

North American Stainless

PLATINUM GROUP METALS THE POWER TO IMPROVE LIVES

General Chemistry I (FC, 09-10) Lab #3: The Empirical Formula of a Compound. Introduction

CATALYSTS IN COMBUSTION TECHNOLOGY AND FLUE GAS CLEANING COMBUSTION AND FUELS

North American Stainless

CBI Product Factsheet: Exhaust Systems in Eastern Europe

EPA Requirements for Diesel Standby Engines In Data Centers. Bob Stelzer / CTO / Safety Power Inc. For 7x24 Fall 2014 Conference. 1.

Reaction of Magnesium with Hydrochloric Acid (Gas Laws) Chemicals Needed:

FACT SHEET PROPOSED MERCURY AND AIR TOXICS STANDARDS

MATHESON STACK EMISSION CALIBRATION PROGRAM. Experience the MATHESON Commitment to Supply Chain Excellence

MILESTONE H E L P I N G C H E M I S T S

DMA-1 Direct Mercury Analyzer

ETV Joint Verification Statement

METHOD 9075 TEST METHOD FOR TOTAL CHLORINE IN NEW AND USED PETROLEUM PRODUCTS BY X-RAY FLUORESCENCE SPECTROMETRY (XRF)

Catalytic Activity of Enzymes

MATHESON REFINERY PROGRAM for Specialty Gas Supply. Experience the MATHESON Commitment to Supply Chain Excellence

CH3 Stoichiometry. The violent chemical reaction of bromine and phosphorus. P.76

NANOCOMPOSIX'S GUIDE TO ICP-MS MEASUREMENT

Experiment 7: Titration of an Antacid

Emission report Honda accord/cu1

What are the causes of air Pollution

EXPERIMENT 12: Empirical Formula of a Compound

Summer Holidays Questions

OLIVÉR BÁNHIDI 1. Introduction

Texture characteristic of membrane materials ASAP, BET

NITRIC OXIDE and NITROGEN DIOXIDE 6014

This article provides a basic primer on an

Understanding Tier 4 Interim and Tier 4 Final EPA regulations for generator set applications

MATERIAL SAFETY DATA SHEET

CONTENTS. ZVU Engineering a.s., Member of ZVU Group, WASTE HEAT BOILERS Page 2

Tips for a Successful Diesel Retrofit Project

EXPERIMENT 4 THE DETERMINATION OF THE CALORIC CONTENT OF A CASHEW NUT

COMBUSTION. By: Michael Biarnes. In collaboration with: Bill Freed and Jason Esteves. E Instruments International LLC -

1.1.2 Polypropylene The polypropylene must be a white opaque film, 1 2 mil thick. Biaxial orientation is preferred.

Technical Report. Automatic Identification and Semi-quantitative Analysis of Psychotropic Drugs in Serum Using GC/MS Forensic Toxicological Database

DETERMINATION OF TOTAL CARBON, TOTAL ORGANIC CARBON AND INORGANIC CARBON IN SEDIMENTS

Physical & Chemical Properties. Properties

PAAM COMMERCIAL PRIVATE LIMITED

Sample preparation for X-ray fluorescence analysis

Chapter 3 Mass Relationships in Chemical Reactions

Measuring volume of gas produced Measuring precipitation (because sulphur is produced) e.g. look for X to disappear Measure mass lost

Innovative Technology Verification Report

ETV Joint Verification Statement

Recovery of Elemental Copper from Copper (II) Nitrate

Part B 2. Allow a total of 15 credits for this part. The student must answer all questions in this part.

VEHICLE INSPECTION FOR REDUCING EMISSION

Chemistry 112 Laboratory Experiment 6: The Reaction of Aluminum and Zinc with Hydrochloric Acid

1. PRODUCT AND COMPANY IDENTIFICATION

Peel Adhesion of Pressure Sensitive Tape

Anodes and Misc Equipment

7. Chemical Waste Disposal Procedures

Honors 227 Fall 2007 Laboratory with Ms. Clark. Enzymes, Reactions, Metabolism and Homeostasis

Carbon Dioxide Membrane Separation for Carbon Capture using Direct FuelCell Systems

MATERIAL SAFETY DATA SHEET

Texas Commission on Environmental Quality Page 1 Chapter Control of Air Pollution from Nitrogen Compounds

1.3 Properties of Coal

Coating and Extraction of Honeycomb Denuders

Aerosol Fire Suppression. Your Choice for Special Hazard Fire Protection

As published in PIM International

2010 NOV 30 P MQ. November 29,2010

Lead in Paint: U.S. Legal Framework Case Study

Weight Loss Determined from Mass Spectrometry Trend Data in a Thermogravimetric/Mass Spectrometer System

ENVIRONMENT CANADA TECHNICAL GUIDANCE DOCUMENT MARINE SPARK-IGNITION ENGINE, VESSEL AND OFF-ROAD RECREATIONAL VEHICLE EMISSION REGULATIONS.

Chapter 1: Moles and equations. Learning outcomes. you should be able to:

Lecture 35: Atmosphere in Furnaces

Taking Apart the Pieces

COMBUSTION. In order to operate a heat engine we need a hot source together with a cold sink

IUCLID 5 COMPOSITION AND ANALYSIS GUIDANCE DOCUMENT: IRON ORES, AGGLOMERATES [EINECS NUMBER , CAS NUMBER ] IRON ORE PELLETS

THE ROLE OF METALLURGY IN ENHANCING BENEFICIATION IN THE SOUTH AFRICAN MINING INDUSTRY

Pesticide Analysis by Mass Spectrometry

Chapter 16: Tests for ions and gases

Solubility Curve of Sugar in Water

RULE DRY CLEANERS USING SOLVENT OTHER THAN PERCHLOROETHYLENE

G8 GALILEO. Innovation with Integrity. High-End Melt-extraction Analyzer. Inert Gas Method

The Relation Between Gasoline Quality, Octane Number and the Environment

FACT SHEET PROPOSED REVISIONS TO THE NATIONAL AMBIENT AIR QUALITY STANDARDS FOR SULFUR DIOXIDE

Elemental Analyses by ICP-AES

CHAPTER 3 EXPERIMENTAL SET UP

Chapter 3 Student Reading

CSUS Department of Chemistry Experiment 8 Chem.1A

Smoke Management Plan

Transcription:

LABORATORY ANALYSIS OF CATALYTIC CONVERTERS LEADS TO BETTER ENFORCEMENT RESULTS SMITH, DON 1, SUGGS, JENNIFER 2, ISIN, AMELIE 3 1 Chemist, National Enforcement Investigations Center, Office of Criminal Enforcement, Forensics and Training, Office of Enforcement and Compliance Assurance, U.S. Environmental Protection Agency, smith.donj@epa.gov 2 Chemist, National Enforcement Investigations Center, Office of Criminal Enforcement, Forensics and Training, Office of Enforcement and Compliance Assurance, U.S. Environmental Protection Agency, suggs.jennifer@epa.gov 3 Program Analyst, Air Enforcement Division, Office of Enforcement and Compliance Assurance, U.S. Environmental Protection Agency, isin.amelie@epa.gov SUMMARY EPA s National Enforcement Investigations Center (NEIC) is a forensic laboratory that also analyzes catalytic converters to determine the compliance of recreational vehicle and motorcycle manufacturers with the Clean Air Act. NEIC has developed some innovative techniques for the measurement of catalyst washcoat loading on motorcycle and recreational vehicle catalytic converters. The catalytic converters present a challenge because the washcoat is tightly bound to a metallic substrate and is physically inaccessible. Physical removal of the washcoat followed by analysis by X-ray fluorescence spectrometry has shown the vast majority of the sampled catalytic converters to be noncompliant, leading to successful EPA enforcement actions against recreational vehicle and motorcycle manufacturers and importers. 1 INTRODUCTION AND BACKGROUND The U.S. Environmental Protection Agency (EPA) s mission is to protect human health and the environment, and this includes responsibilities for air emissions from imported vehicles and engines. The Clean Air Act (CAA) requires imported engines and vehicles to be covered by an EPA certificate of conformity (COC), demonstrating that they meet emission standards. EPA takes action when imported goods are not in compliance with the Clean Air Act. Many of the imported vehicles that have been inspected by EPA are not covered by their COCs because the catalytic converters have been found to be materially different from the design specified in the application for the COC. For this reason, EPA concludes that the source vehicles are uncertified and have been imported in violation of the Clean Air Act. EPA s Mobile Source Enforcement Branch has recently been particularly focused on recreational vehicle and motorcycle cases, given the high rate of noncompliance with CAA requirements in this sector. Laboratory analysis of catalytic converters is critical for EPA enforcement and helps the EPA focus its limited resources on the products that cause the most environmental harm. Vehicles and engines with noncompliant catalytic converters emit higher levels of carbon monoxide, hydrocarbons, and nitrogen oxides that contribute to the formation of ground-level ozone, or smog. Exposure to even low levels of ozone can cause respiratory problems, and repeated exposure can aggravate pre-existing respiratory diseases. In addition, air toxics such as hydrocarbons are known or suspected human carcinogens. 1

Motorcycle and recreational vehicle catalytic converter specifications include the volume of the catalytic converter, the amount of each catalytic metal present, and the number of pores in the converter. The most common catalysts used for pollution control contain metals or metal oxides such as platinum (Pt), palladium (Pd), rhodium (Rh) and vanadium pentoxide (V 2 O 5 ). These catalysts increase the rate at which the incomplete combustion products of carbon monoxide, hydrocarbons, and nitrogen oxides are converted to carbon dioxide, water vapor, and nitrogen. Catalysts provide a reaction site for the molecules and decrease the reaction energy needed to convert the molecules. These metals are mixed with a carrier, such as aluminum oxide, and then deposited on a support that can be either ceramic (automotive catalytic converters) or metal (recreational vehicle or motorcycle catalytic converters). A typical recreational vehicle or motorcycle exhaust catalytic converter consists of a metallic substrate that is coated with an active layer of the carrier, or washcoat. In production, washcoat loading is normally determined by a weight gain procedure. When EPA began its laboratory analysis of catalytic converters in 2008, the agency lacked an established procedure for analysis of recreational vehicle or motorcycle exhaust catalytic converters. EPA refined its sample preparation and X-ray fluorescence spectrometry (XRF) analysis methodology through trial and error. Refinements simultaneously improved the accuracy of results and reduced the time necessary to obtain results, improving the effectiveness of EPA s enforcement response. This paper provides a detailed description of the laboratory techniques EPA is using and the enforcement results EPA has achieved for recreational vehicles and motorcycles based on its catalytic converter analysis work. 2 SAMPLING EPA has, to date, examined catalytic converters from vehicles and engines that were built by more than 18 different manufacturers. Samples are obtained through inspections conducted at retail locations and at U.S. ports. The U.S. Department of Homeland Security s Bureau of Customs and Border Protection (CBP) conducts the portside inspections. Officers identify shipments with particular focus on companies that have previously violated the Clean Air Act, and put them on hold for inspection. EPA investigators, working closely with a special team of CBP officers, then inspect the vehicles and engines. If the vehicles or engines are certified with a catalytic converter, EPA removes the muffler. The catalytic converter samples are then removed from the vehicle muffler, but are left uncut in their original sleeve for mailing to EPA s National Enforcement Investigations Center (NEIC) under chain of custody for analysis. 3 SAMPLE PREPARATION AND PHYSICAL MEASUREMENTS NEIC initially assumed that the internal structure of the motorcycle and recreational vehicle catalytic converters would contain ceramic substrates similar to that of automotive catalytic converters. However, examination of the actual mufflers from motorcycle and recreational vehicles showed they contained a stainless steel honeycomb mesh coated with the washcoat. Manufacturers produce the honeycomb from corrugated stainless steel rolled into a cylinder and encased in a steel tube (Figure 1). 2

FIGURE 1. End View of a Recreational Vehicle or Motorcycle Catalytic Converter Because of this unique configuration, NEIC developed two different strategies to remove the washcoat. NEIC developed the first strategy from a catalytic converter manufacturer that employed a wash procedure using acid and hydrogen peroxide. In this procedure, large volumes of solution containing nitric acid and hydrogen peroxide removed the washcoat containing the precious metals platinum, palladium, and rhodium. The resulting solution was then treated with hydrochloric acid and evaporated to dryness. After several cycles of treatment, the residue was heated to 540 degrees Celsius ( C) in a muffle furnace, then ground. NEIC analyzed the ground material for the precious metal concentrations. NEIC s examination of the stainless steel mesh after the acid and peroxide extractions revealed that a residue of washcoat remained on the honeycomb mesh. Physical manipulation of this mesh yielded additional material, indicating incomplete removal of the washcoat. This led NEIC to develop a procedure to physically remove the washcoat from the catalytic converters. Physical measurements, photographs, and weights were required to ascertain the specifications for the catalytic converters. Metric calipers and rulers were used to measure the height and diameter of the stainless steel mesh and outer pipe. These measurements were used to calculate the area of the mesh monolith and determine the volume of the cylinder. Photographs of the ends of the mesh were taken for pore count measurement. Initial, periodic, and final weights of the samples and separate parts of the samples (outer casing, honeycomb mesh, and washcoat recovered) were recorded during disassembly. After the initial weight was recorded, NEIC used an angle grinder with a metal cutting wheel to cut through the outer casing of the catalytic converter (Figure 2). 3

FIGURE 2. Analyst Cutting the Outer Steel Casing of a Catalytic Converter After the initial cut, NEIC removed the outer pipe to expose the stainless steel mesh that contained the aluminum oxide based washcoat. In many samples, the stainless steel mesh was manually unwound to remove the washcoat. Unwinding the mesh removed a significant amount of washcoat material, which was collected, weighed, and stored. The physical removal was continued until no additional washcoat could be removed. In some other samples, the fabrication of the honeycomb mesh prevented the mesh from unwinding. These samples required disassembly with additional force and also additional care to ensure minimal loss of washcoat. To disassemble these more challenging samples, NEIC placed the tip of an awl into a mesh hole and tapped it with a rubber mallet to break the mesh and release the washcoat. Using these tools, the mesh was reduced to small metal pieces. Both washcoat and metal pieces were collected in weigh boats beneath the samples. A magnet was used to remove metallic fragments from the powder (Figure 3). NEIC investigated a coarse disassembly method that separated the mesh into large chunks instead of small strips. If successful, a coarse disassembly could provide a faster method of disassembly with the same or similar washcoat removal results. After this coarse method was applied, weights were obtained, then the large chunks were reduced further using the fine disassembly method. After the samples were completely reduced using the fine disassembly, weights for the mesh pieces and for the washcoat were taken. A comparison of the weights indicated that a significant amount of washcoat still remained in the mesh after the coarse disassembly method. The more intensive and time-consuming fine disassembly proved to be the better method for removal of the washcoat. 4

FIGURE 3. Removal of Metallic Debris Using a Magnet 4 XRF ANALYSIS NEIC selected XRF to analyze the precious metal content of the catalytic converter washcoat. This technique uses an X-ray source to remove inner shell electrons of the atoms in a sample which in turn are replaced by outer shell electrons. The resulting change in energy causes the atoms to emit X-rays that are characteristic of that element. The emitted X-rays are measured quantitatively by calibrating the instrument with standards containing known concentrations of the elements of interest. XRF was chosen because it is relatively fast, has very high precision, and does not require dissolution of the sample. However, since XRF is a direct measurement analytical tool, sample preparation is critical. The success of the technique depends on how similar the samples are to the calibration standards, both in physical form and in chemical makeup. Washcoat removal frequently yields masses that are too low to utilize standard XRF pressed powder sample preparation techniques. To provide a consistent, stable sample for XRF analysis, the samples are diluted in reagent grade aluminum oxide and a cellulose binder. This mixture of washcoat, aluminum oxide, and cellulose binder is ground with an agate mortar and pestle or using a ball mill and then pressed into a pellet that can be analyzed by XRF. The XRF spectrometer is calibrated using a combination of National Institute of Standards and Technology (NIST) standard reference materials (SRMs) and synthetically prepared standards containing platinum, palladium, and rhodium. Variations in the sample matrix are partially corrected through the use of a Compton scattering correction. 5

5 RESULTS EPA s enforcement efforts are constantly evolving to keep pace with the changing compliance landscape. Currently, EPA is addressing the growing number of recreational vehicle and motorcycle imports from China. To date, almost all of the catalytic converters sampled from these vehicles and sent to the laboratory for analysis have been found to be noncompliant. This may, in part, be due to the rising costs of the precious metals which are critical to catalytic converter efficacy. In 2010, EPA and CBP stopped a total of about 14,000 recreational vehicles, small gasoline-powered engines, and motorcycles at the port because they were not built to the correct certified design. In almost all instances, these vehicles and engines bore labels stating they were certified. EPA inspections, however, found that approximately 80% of the vehicles and engines differed from the certified design in ways that could affect emissions, with about half of the uncertified vehicles and engines having nonconforming catalytic converters. In addition to seizures at the ports, EPA s inspections and analysis work has culminated in several case settlements, the largest of which was against The Pep Boys Manny, Moe & Jack (Pep Boys) and Baja, Inc. (Baja) in May 2010. Pep Boys is a national automotive aftermarket and service chain that operates more than 580 stores in 35 states and Puerto Rico. Baja contracts with manufacturers in the People s Republic of China to supply recreational vehicles and motorcycles to Pep Boys and other U.S. companies. Baja also handles all after-sale functions, such as warranty claims and replacement parts. This case was the largest vehicle and engine importation case brought under the CAA by the U.S. by number of vehicles and engines affected and penalty paid. The case involved the importation of at least 241,000 illegal vehicles and engines over a six year period, and resulted in a $5 million civil penalty. At its peak, Pep Boys was the third largest importer of Chinese-made all-terrain vehicles in the U.S. All of the catalytic converters analyzed in support of the Pep Boys case were found to be noncompliant. In June 2010, EPA settled another imports case against Taotao USA, Inc. (Taotao) involving noncompliant catalytic converters. Taotao and its predecessor, AIMX Industry, Inc., d.b.a./a.k.a. AIM-EX Industry, Inc., or Vicoo Industry, Inc, imported thousands of illegal recreational vehicles into the U.S. between 2008 and 2010. In addition, Taotao was the largest importer last year of Chinese-made all-terrain vehicles in the U.S. The settlement required Taotao to pay a $260,000 penalty and implement a rigorous corporate compliance plan, including regular catalytic converter testing. On-road and off-road vehicles and engines emit roughly half of the U.S. air pollution. Importing vehicles and engines without proper emission controls is not only detrimental to human health and the environment; it also provides an unfair competitive advantage to the manufacturers of noncompliant products. To address the myriad and expanding number of ways in which vehicles and engines can be noncompliant, EPA will continue to innovate and explore new laboratory procedures in support of enforcement cases to ensure that products imported and sold in the U.S. comply with the Clean Air Act. 6

6 BIBLIOGRAPHY EPA FACTSHEET: Air Toxics from Motor Vehicles, U.S. Environmental Protection Agency, available at http://www.epa.gov/oms/f02004.pdf. Heck, R. M., Farrauto, R. J., and Gulati, S. T., Catalytic Air Pollution Control: Commercial Technology, 2 nd ed., 2002, pp. 3-24, 69-73. The Pep Boys Manny, Moe & Jack and Baja, Inc. Settlement, U.S. Environmental Protection Agency, available at http://epa.gov/compliance/resources/cases/civil/caa/pepboys.html. US EPA Clean Air Act Mobile Source Importation Settlement Information, U.S. Environmental Protection Agency, available at http://cfpub.epa.gov/compliance/civil/programs/caa/importation/. 7