Impact Study on Mobile Cranes

Similar documents
New Ultra Low Sulfur Diesel fuel and new engines and vehicles with advanced emissions control systems offer significant air quality improvement.

EUROPEAN COMMITTEE UNDER THE GOVERNMENT OF THE REPUBLIC LITHUANIA. September 5, 2001 Final report summary

Operational eco-efficiency in Refineries

A comparison of the impacts of Euro 6 diesel passenger cars and zero-emission vehicles on urban air quality compliance

COATING YOUR WAY TO LOWER EMISSIONS

Marin gas logistics. Work package 5. D5-5 Environmental studies - assessment of air emissions in terminal ports

COMMISSION REGULATION (EC)

WLTP for fleet. How the new test procedure affects the fleet business

COMMISSION DELEGATED REGULATION (EU) /... of

Proportion of the vehicle fleet meeting certain emission standards

Heavy-Duty Low-NOx and Phase 2 GHG Plans

POST 2020 VEHICLE CO 2 EMISSIONS POLICY

Official Journal L 076, 22/03/2003 P

Pioneering MTU C&I diesel engines for U.S. EPA Tier 4

DG CLIMA studies on CO2 emissions from vehicles

Subject: ACEA proposal for Euro 6 OBD and Euro 6 PN limit for gasoline direct injection engines.

TRUCK MANUFACTURERS: BUSINESS MODEL RISKS FROM ALTERNATIVE DRIVETRAINS THE ROAD TOWARDS EMISSIONS REDUCTION. Joachim Deinlein and Romed Kelp

Q&A ON EMISSIONS TESTING

Summit County Greenhouse Gas Emissions Summary, 2017

Proposal for a DECISION OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL

Low Sulphur Fuel Oils Preliminary Estimated Costs to Canadian Industry based on European Data

Capabilities of Emission Control Technologies and their Impact on Air Quality. Expert Meeting of the EU Refining Forum Brussels 1 December 2017

Academia, Industry and Government: together for automotive engineering development

The topic of exhaust emission regulation and reduction is extremely complex. In order to comply with the permissible emission values, increasingly

R&D: FUTURE-PROOFING THE BMW GROUP. DR. HERBERT DIESS MEMBER OF THE BOARD OF MANAGEMENT OF BMW AG, DEVELOPMENT

GLOBAL REGISTRY. Addendum. Global technical regulation No. 5

The Introduction of Euro 5 and Euro 6 Emissions Regulations for Light Passenger and Commercial Vehicles

Proposal for a DIRECTIVE OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL

Aging of the light vehicle fleet May 2011

PRESS RELEASE 09:00 GMT, 6 th March 2018 London, UK

IAPH Tool Box for Port Clean Air Programs

COMMISSION DELEGATED REGULATION (EU) /... of

Press release (blocking period: , 6:00) Industry Study. E-Mobility 2019: An International Comparison of Important Automotive Markets.

Thema der Arbeit. Discussion of IT-infrastructure for electric mobility. Bachelorarbeit. vorgelegt von. Patrick-Oliver Groß

Transitioning to low carbon / low fossil fuels and energy sources for road transport

Non-Road Mobile Machinery EU Regulation

COUNCIL OF THE EUROPEAN UNION. Brussels, 11 December /3/06 REV 3 ADD 1. Interinstitutional File: 2003/ 0153(COD) ENT 84 CODEC 561

COMMISSION OF THE EUROPEAN COMMUNITIES REPORT FROM THE COMMISSION. Quality of petrol and diesel fuel used for road transport in the European Union

Recommendations of the Expert Group on Preventing Motorcycle Injuries in Children

DANIEL LEUCKX. Recent and proposed legislative developments. PLATTS, Middle Distillates 4 th Annual Conference. Policy Executive, EUROPIA

Environmental and EnergyStrategies for Freight Transport. Dipl.-Ing. Håkan Samuelsson, Chairman of the MAN Nutzfahrzeuge Gruppe

FUEL CELL POWERED INDUSTRIAL TRUCK APPLICATION IN THE BMW PLANT LEIPZIG. A NEW BENCHMARK? ANALYSIS AND REPORTING.

Benefits of greener trucks and buses

Recent Developments In The German Biodiesel Market And Implications For Investment Projects

September 21, Introduction. Environmental Protection Agency ( EPA ), National Highway Traffic Safety

COMPROMISE AMENDMENTS 1-18

Cars and vans CO2 regulations: even ambitious EU standards deliver less than half transport emission reductions needed to meet 2030 climate targets

Focus on the Future Powertrain Strategies for the 21st Century

EUROPEAN PARLIAMENT Committee on the Environment, Public Health and Food Safety

Embargoed until: March 5, 2019, 7 a.m. CET. Key Financial Data: January 1 to December 31, Evonik more robust as strategy takes effect

A CO2-fund for the transport industry: The case of Norway

What s steering the UAE s automotive aftermarket?

Diesel The new number game in town. Centre for Science and Environment

EN 1 EN COMMISSION OF THE EUROPEAN COMMUNITIES. Brussels, xxx C(2008) YYY. Draft COMMISSION REGULATION

Potential Impact of a Green Tire Regulation

Fuel Cell Application in a New Configured Aircraft PUBLISHABLE REPORT

Insights into WLTP and RDE

The IAM in Pre-Selection of global automotive trends impacting the independent multi-brand aftermarket

GEME WG Presentation of recommendations for full amendment of Directive 97/68/EC

Periodic Technical Inspection to Control Emission of Pollutant

Chief Operating Officer. Nigel Bell, Energy Resource Manager

Real Driving Emissions

Study Results Review For BPU EV Working Group January 21, 2018

Electric energy storage Elia Group Approach

CONTACT: Rasto Brezny Executive Director Manufacturers of Emission Controls Association 2200 Wilson Boulevard Suite 310 Arlington, VA Tel.

EVREST: Electric Vehicle with Range Extender as a Sustainable Technology.

Optimization Solutions in Thermal Power Plants

Furnace-based optimisation of a lignite-fired steam generator

1. My vehicle is affected. Do I need to take it to a workshop immediately?

Draft COMMISSION DECISION

Tyre noise limits of EC/661/2009 and ECE R117: Evaluation based on sold tyres in the Netherlands

SUMMARY OF THE IMPACT ASSESSMENT

GERMAN AMERICAN WIND ENERGY BUSINESS CONFERENCE Trends in Supply Chain and After Sales fr a Component Manufacturer s Perspective

GT-Suite Users International Conference Frankfurt a.m., October 22 nd 2012

Experimental Investigations on a Four Stoke Diesel Engine Operated by Jatropha Bio Diesel and its Blends with Diesel

***I DRAFT REPORT. EN United in diversity EN 2011/0190(COD)

Transmission Grid Development & Investment Planning on EHV Level in Germany

Merger of the generator interconnection processes of Valley Electric and the ISO;

FREQUENTLY ASKED QUESTIONS TIER 4 INTERIM / STAGE IIIB PRODUCTS

The new EU-NRMM-Regulation

City of Palo Alto (ID # 6416) City Council Staff Report

Particle number emission limits for Euro 6 positive ignition vehicles (PI)

In Conversation with: Vivian Balakrishnan, Singapore s Minister for the Environment and Water Resources (MEWR)

GIBRALTAR ERDF OPERATIONAL PROGRAMME POST ADOPTION STATEMENT

Young Researchers Seminar 2015

PwC Autofacts. The Transformation of the Automotive Value Chain.

Regulatory Announcement

Implementation of Future Transportation Technologies: Getting Beyond the Low Hanging Fruit without Chopping Down the Tree

Regeneration of the Particulate Filter by Using Navigation Data

DemoEV - Demonstration of the feasibility of electric vehicles towards climate change mitigation LIFE10 ENV/MT/000088

Department of Legislative Services

Emission from vehicles with Euro 6/VI technology. Results from the measurement program in EMIROAD 2015

Frequency-Regulation Reserves by DERs: barriers to entry and options for their resolution. Olivier BORNE - Marc PETIT - Yannick PEREZ

Industrial machinery and heavy equipment. Hatz Diesel. Developing a water-cooled industrial engine with the help of Siemens PLM Software

ANNUAL GENERAL MEETING. Cologne, 30 April 2009

Case No COMP/M DAIMLERCHRYSLER / DETROIT DIESEL CORPORATION. REGULATION (EEC) No 4064/89 MERGER PROCEDURE

Briefing. German manufacturers calling for weaker car fuel efficiency targets. Context. July How are car CO 2 emissions regulated?

Recent Development in Energy Efficiency Policy in the EU

Dependable Power. Every Track. Engines For Maintenance Of Way.

Adiabatic Compressed Air Energy Storage in Context of the Markets

Transcription:

Impact Study on Mobile Cranes Emissions Inventory and Impact Assessment Directive 97/68/EC: Projection into a Change from Stage IV to V and Transition from Stage III A to III B and III B to IV

Editor: Authors: Prof. Dr.-Ing. Dipl.-Wi.-Ing. W. A. Günthner fml Lehrstuhl für Fördertechnik Materialfluss Logistik Technische Universität München Boltzmannstr. 15 85748 Garching www.fml.mw.tum.de Willibald A. Günthner Julia Freis Matthias Amberger Date: 15. December 2014 Prepared for: Copyright FEM Product Group Cranes & Lifting Equipment, Subgroup Mobile Cranes Lyoner Straße 18 60528 Frankfurt/Main www.fem-eur.org fml Lehrstuhl für Fördertechnik Materialfluss Logistik Translated from the German by Heinz-Klaus Lüdersen Printed in Germany 2015

With the proposal [COM (2014) 581] for a renewal of the present Directive 97/68/EC regarding emission limit values for combustion engines in non-road mobile machinery, the European Commission envisages a new stage (Stage V) with more stringent limit values for exhaust gas emissions. The mandatory application date within the engine power range 130 560 kw of the Stage V is 1 January 2019. Machine manufacturers, who install these engines into their machines, have 12 months' time from this date to adapt their machines to the new Stage V engines, followed by 6 months sell-off period. Previous transition regulations allowed the machine manufacturers considerably more time and flexibility for the adaption of their machines. The shorter adaption time confront the manufacturers of mobile cranes with problems. Due to technical reasons these consider themselves not in a position to convert their diverse product portfolio to a new emission stage within 12 months. The engines are deeply integrated in the machines. That has the consequence that for any changes to the engine and exhaust gas aftertreatment system; the mobile cranes must go through a technically complex and time consuming redesign. To predict both, the necessary expenditure and the environmental impact for the conversion to the Stage V, the initial conversion of the all-terrain crane from Stage III A to III B and from Stage III B to IV was exemplarily investigated. The data for the study were collected from the four largest European mobile crane manufacturers. Jointly they have a market share of 94 % for all-terrain cranes in Europe. The results show, that the manufacturers with their existing resources were up to now in a position to convert approximately 40 all-terrain crane models within 4.5 years. This timeframe includes the conception phase without having a new engine available. The time from when serial engines are available for the manufacturers, where no more changes need to be made, is decisive for the conversion period. Based on experience, these completed engines are available approximately 6 to 3 months prior to expiry of the old stage. From this date, the manufacturers need more than two years to adapt all of their models to the new engines and exhaust gas aftertreatment systems for the superstructures and the carriers. The costs for this amount to 37.76 million for the conversion from Stage III A to III B. For the conversion from Stage III B to IV until the end of the conversion phase beginning of 2016, they will amount to 56.79 million, according to the manufacturers estimates. Calculations for the emission inventory of all-terrain cranes show that in Europe their share of total nitrogen oxide and particle emission from non-road mobile machinery is relatively low. In the year 2020, all-terrain cranes are responsible for a share of 0.38 % of the nitrogen oxide emission of mobile machines and devices. The same I

applies to the particle emission; here in the year 2020 all-terrain cranes will contribute 0.57 % to the total particulate emission of mobile machines and devices. To investigate the impact of an extension of the transition period at all-terrain cranes on the environment, health and society for the conversion to Stage V and to quantify the necessary economic effort, different scenarios were generated and compared. Initial data for the pending changes to the engine and exhaust gas aftertreatment system were collected from the three engine manufacturers, representing 100 % of the suppliers for all-terrain crane engines to the considered manufacturers. According to the information provided by the engine manufacturers, a diesel particle filter will be added, which up to now, is installed on no engine exhaust gas aftertreatment for European mobile cranes. The volume of the present exhaust gas aftertreatment system will increase by about 20 % and the weight will rise by up to 100 kg. The serial production of the new engines is planned from the middle of 2018. Thus earliest availability of completed engines is mid / end of 2018 for the crane manufacturers. Based on this data, the mobile crane manufactures forecasted necessary design adaptations for their all-terrain cranes. According to the manufacturers, a time period of approximately 3 years from the availability of serial engines for the conversion to Stage V is needed to perform the estimated alterations. As both the design work and the necessary time needed are of a similar level as for the conversion from Stage III A to III B, the companies expects cost burden in a similar amount of 34.06 million. The following scenarios were generated based on the prognosis of the manufacturers in order to calculate and compare the impact of these scenarios on the environment and health / society within the frame of a Trend Impact Analysis and a Cost Effectiveness Analysis for the time horizon 2020 to 2050: Scenario 1: Business-As-Usual-Scenario (BAU) without implementation of Stage V, serves as a benchmark for the following scenarios with implementation of Stage V. Scenario 2: Implementation of Stage V with a compulsory transition phase of 12 months according to [COM (2014) 581] and a conversion time frame, ideally of 12 month, with the result that from 2020 only cranes with Stage V are sold in the European Union. Scenario 3: Implementation of Stage V with a transition phase of 36 months for mobile cranes and a conversion time frame in the normal case of 36 months, with the result that from 2020, one third of the cranes are sold with Stage V and two thirds with Stage IV in the European Union; from 2021, two thirds are sold with Stage V and one third with the Stage IV; from 2022 all cranes are sold with Stage V. Scenario 4: Implementation of Stage V with a compulsory transition phase of 12 months according to [COM (2014) 581], and a conversion time frame in the normal II

case of 36 months with the result, that from 2020, one third of the cranes are sold with Stage V and none with the Stage IV are sold in the European Union; from 2021 two thirds of the cranes with Stage V and none with Stage IV; from 2022 all cranes with Stage V. Non-converted crane models are not available in the years 2020 and 2021. The calculations of the Trend Impact Analysis on the impacts on the environment show for the scenarios that the duration of the transition phase for the implementation of the Stage V can have significant implications regarding the emissions. With a too short time frame, as in Scenario 4, not all cranes can be converted by the end of the transition phase and thus cannot be sold. This means that old machines with higher exhaust emission cannot be replaced by newer ones and thus must stay longer in the population. In the short term, emissions would therefore even increase in the early stages of Stage V. This issue is confirmed by the particle emissions calculated for each year. These are, in the year 2020 for Scenario 2 at 347 t which corresponds to a share of 0.57 % of the total particle emission from mobile machinery and devices; for Scenario 3 are 348 t with a share of likewise 0.57 %; and for scenario 4 are 366 t with a share of 0.61 %. The differences between a transition phase of three years compared with one year are only marginal. Finally, the same low particle emission level of 18 t in the year 2050 is maintained with all conversion scenarios. By the continuous reduction of the particle emission from diesel engines other sources of particle emission like tyre abrasion, brake wear, etc. will constitute the dominant emission sources in the future. Already today the particulate matter emissions from the tyre abrasion for a modern all-terrain crane with Stage IV shows a similar high value like the engine-generated particulate matter emissions from the travel operation. The Cost Effectiveness Analysis shows, that the cost-benefit-ratio for the introduction of an emission Stage V for all-terrain cranes for the scenarios 2, 3 and 4 is negative by more than minus 70 %. Here the engine and mobile crane manufacturers accrue the costs of 66 million. The generated benefit is to be the avoidance of emitted air particulate matter. The real benefit here is achieved by prevention of health costs for the society caused by particle emissions. In comparison to the arising costs, this benefit for the society (avoided damage costs) is relatively low with 17 for scenario 2 and 16 million for scenario 3 as well with about 6 million for scenario 4. It must be recognized, however, that the time frame for the transition phase as in scenario 4 has a high impact on the social benefit. Download complete Impact Study on Mobile Cranes: http://www.fml.mw.tum.de/fml/index.php?set_id=870 III