VERT-Suggestions for «post Euro 6»

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9.VERT Forum EMPA Academy 14.3.2019 VERT-Suggestions for «post Euro 6» A. Mayer 1

A VERT Contribution based on to EU Court of Auditors Workshop on «EU-Response to Dieselgate» Luxembourg 2.Oct.2018 Report published Feb.2019 EU-Actions needed to introduce, enforce and preserve Best Available Technology for Elimination of Toxic Air Contaminants Emitted by Internal Combustion Engines 2

The following actions are urgently needed and the required technology is readily available New PTI to detect DPF & SCR failures and manipulations Strengthen PN criteria, also for NRMM Emission Upgrade for the in-use fleet by OEM Banning highly toxic secondary emissions and metals Unify metrics for exhaust and ambient pollution Address PN exposure in vehicle cabins

and this is what we are sometimes finding - why because they want to avoid cost for proper repair or cleaning

DPF Failure Statistics in Switzerland Measurments by Beat Gloor AWEL 2017 Each damaged or manipulated DPF/GPF emits 100-1000 times more particles than he properly maintained DPF/GPF

Correlation of NEDC-cycle type approval with low idle PTI by G.Kadijk, TNO (Source: TNO - 21. NPC ETH Zürich) 6

Portable Particle Number Emission Instruments are available: CPC as well as DC NANEOS TSI TSI NPET (certified by METAS) TESTO PEPA (Source: B.Gloor, AWEL) 7

SCR-TEST requires either a Chassis Dyno or (speculated) a Temperature Step at elevated idle by Temperature Management Tools like intake throttle Chassis dyno load / speed step Diesel-LDV, Euro 6, AGR, DOC, DPF, SCR 8

The following actions are urgently needed and the required technology is readily available New PTI to detect DPF & SCR failures and manipulations Strengthen PN Emission and Ambient Air Limit Values Emission upgrade for the in-use fleet by OEM Banning highly toxic secondary emissions and lube metals Unify metrics for exhaust and ambient pollution Address PN exposure in vehicle cabins

PM/PN limits at the exhaust and in ambient air are far to high and must be strengthened In today s European policies and the understanding fo the public the health impact of NOx is over-estimated and the health impact of solid ultrafine particles is by far under-estimated 1

DPF Technology permits limit strengthening by > one order of magnitude 99 % efficiency 99.9 % efficiency 99.99 % efficiency 99.999 % efficiency Swiss Statistics for Construction Machines with DPF Source BAFU

The following actions are urgently needed and the required technology is readily available New PTI to detect DPF & SCR failures and manipulations Strengthen PN criteria also for NRMM Emission upgrade of the in-use fleet Retrofit of first fit Banning highly toxic secondary emissions and metals Unify metrics for exhaust and ambient pollution Address PN exposure in vehicle cabins

Emission Upgrade for the in-use Fleet by Retrofit and First Fit EU Parliament has requested a report on Retrofit Measures of the in-use fleet at highly poluted spots by end of 2018. This Report is delayed and no action has been taken EU could also implement a Upgrade Mandate for automotive suppliers to provide for each class an emission upgrade option for LEZ 13

The following actions are urgently needed and the required technology is readily available New PTI to detect DPF & SCR failures and manipulations Strengthen PN criteria, also for NRMM Emission upgrade for the in-use fleet by OEM Ban highly toxic secondary emissions and lube metals Unify metrics for exhaust and ambient pollution Address PN exposure in vehicle eabins

Toxicity requires to specify Chemistry The US Clean Air Act 202 requires since 1970 that new technology is not introducing additional toxic substances same in Switzerland since EJPD 1990 EU uses non-differenciating definitions NOx, HC and PM and is thus not addressing extremely toxic substances as part of these EU must at least address NO 2 as part of NOx PAH as part of HC Metals (from lube oil and wear) as part of PM

The benzo(a)pyrene example (carcinogenic) Euro-5 GDI vehicles ng/nm 3 Benzo(a)pyrene ~ 1000x higher Diesel emissions BaP 78-92 ng/nm 3 without DPF non-coated coated coated non-coated < 10 ng/nm 3 with DPF (Mean values) Directive 2004/107/EC BaP target value in ambient air: 1 ng/m 3 1

The following actions are urgently needed and the required technology is readily available New PTI to detect DPF & SCR failures and manipulations Strengthen PN criteria, also for NRMM Emission upgrade options for the in-use fleet by OEM Ban highly toxic secondary emission and lube metals Unify metrics for emission and ambient pollution Address PN exposure in vehicle cabins

PN and/or EC show the Truth PM10 did only change by 18% over this period but in some years it did even increase due to construction works PM10 does not reflect traffic emission so why use it and not change to EC or PN?

The Problem: and ambient Air Criteria? Measurements in China: Phänomene zeigen: Daten aus der Literatur und von Mayer 20.12.2012 90-120.000 PN/cm³ at reported PM2.5 >300µg/m³ unhealthy air Ursachen: Kammerexperiment Etwas Theorie: binäre Koagulation 18.12.2013 200.000-500.000 P/cm³ at reported PM2.5 <50µg/m³ healthy air?? Modell von Mingzhou Schlussfolgerungen Apparent disconnect between PN number concentrations and PM concentrations in highly polluted atmospheres Which metric characterizes health effects best?

The following actions are urgently needed and the required technology is readily available New PTI to detect DPF & SCR failures and manipulations Strengthen PN criteria also for NRMM Emission upgrade options for the in-use fleet by OEM Ban highly toxic secondary emission and lube metals Unify metrics for exhaust and ambient pollution Address PN exposure in vehicle cabins

2 1

Results from Airparif 2007 In Cabin compared to Curbside [μg/m 3 ] Behind a Truck 22

TheUnwanted Nanopassenger by M.Kasper CARB study (S. Fruin): Particle Number PN in the cabin up to 15 x curbside Munich: PN in the car cabin up to 10 x curbside Paris: PN in the car cabin up to 20 x curbside Cabin Air is heavely influenced by emission of cars and trucks driving in front Very High Exposure of Professional Drivers, Users of Public Transport, Scoolbus Passengers

VERT Cabin Filter: "NanoCleaner"

Doors shut, Filter ON... 1.E+04 9.E+03 inside vehicle number concentration (#/cm3) 8.E+03 7.E+03 6.E+03 5.E+03 4.E+03 3.E+03 2.E+03 1.E+03 Filter 3 min outside 0.E+00 100 200 300 400 500 600 700 800 time (s)

The following actions are urgently needed and the required technology is readily available New PTI to detect DPF & SCR failures and manipulations Strengthen PN criteria also for NRMM Emission upgrade options for the in-use fleet by OEM Ban highly toxic secondary emission and lube metals Unify metrics for exhaust and ambient pollution Address PN exposure in vehicle cabins Introduce alcylate (benzene free) fuel for handheld tools