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논문 기본 정보

자료유형
학위논문
저자정보

장원욱 (고려대학교, 고려대학교 대학원)

지도교수
朴深秀
발행연도
2017
저작권
고려대학교 논문은 저작권에 의해 보호받습니다.

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이 논문의 연구 히스토리 (3)

초록· 키워드

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State-of-the-art diesel engines are now widely used for light-duty passenger cars due to its high efficiency and driveability, even by recognition for its environmental friendliness. The introduction of common-rail fuel system, variable geometry turbocharger, highly precise injector, diesel particulate filter and advanced fuelling logic is making diesel engines from dirty, noisy, slow into clean, powerful, pleasant ones. In Europe and South Korea, diesel cars are now very popular among various vehicle purposes.
European Union, where the share of the diesel vehicles in passenger car segment are over 50%, leads world’s pollutant regulation for diesel cars with Euro-series emission regulation standards. In case of particulate matter emissions, the regulation limit was 0.025g/km in Euro 4, the limit is now 0.045g/km in Euro 6. To meet this regulation, most of diesel vehicles are equipped with particulate filters nowadays. On the other hand, the nitrogen oxides (NOx) emission standard of Euro regulation diminished from 0.50g/km in Euro 4 to 0.18g/km in Euro 5 by 64%. Although all the vehicles on the road now satisfy the NOx limit in the vehicle emission certification test, many researchers have insisted that the vehicles emit much more NOx to the atmosphere when they are out of the certification facilities. Nitrogen oxides cause acid rain, photochemical smog and forming ozone in the air which triggers respiratory diseases and eye problems to humans so that it is needed to be regulated strictly.
Due to the limited vehicle test capability of laboratory certification tests, new vehicle certification techniques in and out of the testing facilities were developed and will be deployed in September 2017 with implementation of Euro 6c. First, in-door test New European Driving Cycle (NEDC) procedure will be replaced with Worldwide Harmonized Light-duty vehicle Test Procedure (WLTP), which represents more likely to the real-world driving conditions. Second, Real Driving Emission of Light Duty Vehicle (RDE-LDV) category will be added to the vehicle certification. Therefore, almost every diesel vehicles in future will needed to be equipped with de-NOx after-treatment systems, so the importance of the characteristics of after-treatment systems is getting critical.
Four vehicles categorized as Euro 6b were tested with WLTP in the laboratory and on-road vehicle RDE testing route in Seoul vicinity in some different conditions to investigate the engine-out NOx emission characteristics and the after-treatment system performance. With the test results, the de-NOx performance of catalysts itself and its temperature-caused effect along with raw-NOx emission characteristics will be discussed with two kinds of NOx after-treatment systems - Lean NOx Trap (LNT) and Selective Catalytic Reduction (SCR) system. The raw-NOx characteristics and a datum for minimum RDE compliance due to the temperature and engine operating conditions will also be handled.
The vehicles test were carried in and out of the laboratory. The WLTP test and some other test protocols were performed with ambient temperature of 23℃, 14℃ and -7℃ to confirm the temperature effect. Meanwhile, they were tested through the RDE-LDV test route composed of urban, rural and motorway sections. The NOx sensors were fitted to the several points of the vehicle’s exhaust systems for monitoring the NOx concentration and its reduction performance, Portable Emission Measurement System (PEMS) was used in the RDE-LDV test to measure the various gaseous emissions at the tailpipe of the vehicle.
The vehicle test results show that the engine-out NOx emissions are directly affected by the ambient temperature and the driving tendency. If the temperature of the intake air varies from the standard condition, the NOx emission will rise dramatically. And there are particular load band where the NOx formation rate is notably high. The performance of de-NOx after-treatment systems are also affected by the temperature. The NOx reduction ratio of LNT on regeneration phase were critically related to the catalyst and exhaust gas temperature. The overall NOx reduction ratio of LNT is decided by the capacity of the catalyst and exhaust gas temperature. On the other hand, the SCR system has relatively low-sensitivity to the temperature compared to the LNT system, which shows better NOx reduction performance even in cold-start conditions.

목차

Abstract ⅰ
목 차 ⅳ
List of Tables ⅷ
List of Figures ⅹⅲ
Nomenclature ⅹⅹⅲ
제 1 장 서 론 1
1. 연구 배경 1
1.1. 대기질 개선을 위한 자동차 배출가스 규제 1
1.2. 인증 시험과 실도로 주행 시 질소산화물 4
2. 연구 목적 8
제 2 장 관련 연구 동향 및 이론 10
1. 관련 연구 동향 10
1.1. 현행 인증시험모드 외 운전조건에서의 배출가스 연구 10
1.2. WLTP-NEDC 상관성 연구 13
1.3. RDE-LDV 19
1.4. 임의설정 장치 (Defeat Device) 24
2. 관련 이론 27
2.1. 경유 엔진에서의 NOx 생성 및 배출 원리 27
2.2. 경유자동차 NOx 저감 장치 30
2.2.1. 선택적 촉매 환원법 (SCR; Selective Catalytic Reduction) 32
2.2.2. NOx 흡장 촉매 (LNT; Lean NOx Trap) 35
2.3. 배출가스 인증 시험법 ? WLTP 41
2.3.1. 배출가스 인증 시험 절차 41
2.3.2. 대기오염물질 계산 및 보정법 49
2.4. RDE-LDV 시험법 및 결과 도출 53
2.4.1. RDE-LDV 시험 요건 53
2.4.2. 이동식 배출가스 측정장치 (PEMS; Portable Emission Measurement System) 55
2.4.3. 배기가스 측정 시험 56
2.4.4. 이동식 배출가스 측정장치 검증 57
2.4.5. 이동평균구간법 (MAW; Moving Average Windows) 에 의한 동적 조건 검증 58
2.4.6. 출력빈도수 방법 (Power Bin) 에 의한 동적 조건의 검증 68
제 3 장 실험 장치 및 방법 79
1. 시험 차량 제원 79
2. 이동식 배출가스 분석 장치 82
3. NOx 센서 및 기록기 (NOx Logger) 85
4. 실도로 시험 경로 86
4.1. 경로 A (Route A) 86
4.2. 경로 B (Route B) 89
4.3. 경로 C (Route C) 91
4.4. 경로 D (Route D) 93
제 4 장 결과 및 고찰 96
1. 국제 조화 소형차 시험 사이클 (WLTC) 주행 특성과 배출가스 특성 96
1.1. LNT 장착 차량 98
1.1.1. 대기온도 23℃ WLTC 배출가스 시험 99
1.1.2. 대기온도 14℃ WLTC 배출가스 시험 104
1.1.3. 대기온도 ?7℃ WLTC 배출가스 시험 106
1.2. SCR 장착 차량 111
1.2.1. 차량 3 WLTC 시험 결과 111
1.2.2. 차량 4 WLTC 시험 결과 113
2. 이동식 배출가스 분석기 상관성 검증 116
3. 실도로 주행 시 NOx 배출 특성 119
3.1. 시험차량 1 119
3.1.1. 경로 A 시험 결과 및 분석 122
3.1.2. 경로 D 시험 결과 및 분석 138
3.2. 시험 차량 2 144
3.2.1. 경로 A 시험 결과 및 분석 146
3.2.2. 경로 B 시험 결과 및 분석 163
3.2.3. 차량 2 실도로 배출가스 시험 결과 201
3.3. 시험 차량 3 207
3.3.1. 경로 B 시험 결과 및 분석 210
3.3.2. 경로 C 시험 결과 및 분석 223
3.4. 시험 차량 4 232
3.4.1. 경로 B 시험 결과 및 분석 234
제 5 장 결론 256
참고 문헌 262

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