• Ei tuloksia

Adaptation of Black Carbon Footprint Concept Would Accelerate Mitigation of Global Warming

N/A
N/A
Info
Lataa
Protected

Academic year: 2022

Jaa "Adaptation of Black Carbon Footprint Concept Would Accelerate Mitigation of Global Warming"

Copied!
7
0
0

Kokoteksti

(1)

Adaptation of Black Carbon Footprint concept

1

would accelerate mitigation of global warming

2

Hilkka Timonen1,*, Panu Karjalainen2, Pami Aalto3, Sanna Saarikoski1, Fanni Mylläri2, Niko 3

Karvosenoja4, Pasi Jalava5, Eija Asmi1, Päivi Aakko-Saksa6, Natalia Saukkonen7, Teemu Laine7, 4

Karri Saarnio1, Niko Niemelä2, Joonas Enroth8,Minna Väkevä8,Pedro Oyola9, Joakim Pagels10, 5

Leonidas Ntziachristos11, Raul Cordero12, Niina Kuittinen2, Jarkko V. Niemi13, Topi Rönkkö2 6

1 Atmospheric Composition Research, Finnish Meteorological Institute, P.O. Box 503, FI-00101 7

Helsinki, Finland 8

2 Aerosol Physics Laboratory, Physics Unit, Tampere University, P.O. Box 692, 33014 Tampere, 9

Finland 10

3 Politics Unit, Faculty of Management and Business, 33014 Tampere University 11

4 Finnish Environment Institute (SYKE), P.O. Box 140, FI-00251 Helsinki, Finland 12

5 Inhalation toxicology laboratory, Department of Environmental and Biological Sciences, 13

University of Eastern Finland, P.O.Box 1627, 70211 Kuopio, Finland 14

6 VTT Technical Research Centre of Finland, P.O. Box 1000, 02044 VTT Espoo, Finland 15

7 Cost Management Center, Industrial Engineering and Management, Tampere University, 33720 16

Tampere 17

8 Airmodus Ltd, FI-00560 Helsinki, Finland 18

9 Centro Mario Molina Chile, 7510121, Santiago, Chile 19

10 Division of Ergonomics and Aerosol Technology, Lund University, Box 118, 22100, Lund, 20

Sweden 21

11 Mechanical Engineering Department, Aristotle University Thessaloniki, P.O. Box 458, GR 22

541 24 Thessaloniki, Greece 23

12 Departamento de Física, Universidad de Santiago de Chile, Chile 24

13 Helsinki Region Environmental Services Authority (HSY), P.O. Box 100, FI-00066, Helsinki, 25

Finland 26

27

*Corresponding author 28

KEYWORDS: Black Carbon, Black Carbon Footprint, climate, health 29

(2)

The world urgently needs fast-tracked solutions to combat global warming, and to this end we 30

propose the rapid adoption of the concept of Black Carbon Footprint (BC Footprint), analogous to 31

CO2 Footprint. Carbon footprint is already a well-established concept aiming to describe the 32

climatic effects of atmospheric carbon dioxide (CO2) and Greenhouse gas emissions. However, no 33

such concepts exist for particulate BC emissions despite their climate and health impacts. The BC 34

Footprint concept would be an efficient tool for BC emission mitigation and impact assessment 35

and would support the development of new BC emission mitigation technologies and emission 36

reduction policies.

37

In the Paris Agreement (Article 3, Paris Agreement (2015)), 174 States and the European Union 38

have committed to undertake ambitious efforts to mitigate global warming. The most important 39

atmospheric climate forcers, carbon dioxide (CO2), methane and black carbon (BC), differ from 40

each other in several respects. CO2 and methane are gaseous compounds with relatively long 41

atmospheric lifetimes (years to decades), while BC is a primary particulate emission with a 42

relatively short atmospheric lifetime (days to weeks). It originates mainly from anthropogenic 43

combustion sources, such as transportation, industry and residential combustion (Fig 1).

44

Atmospheric BC consists mostly of agglomerated ultrafine particles, effectively absorbing solar 45

radiation over a large wavelength range, and capable of being transported with air masses over 46

large distances (1). However, due to the limited atmospheric lifetime and unevenly distributed 47

sources, atmospheric BC is characterized by large spatial and temporal variation. In the 48

atmosphere, BC particles can change during ageing process via particle growth and surface 49

reactions (Figure 1). In addition to direct warming impacts, BC can deposit on snow and ice leading 50

to reduction of the earth’s surface albedo. This emphasizes the importance of BC emission and 51

induced warming in the Arctic and generally over northern latitudes (1,2). In urban areas, BC 52

(3)

significantly affects public health and air quality. Recent studies have highlighted BC as stronger 53

and in some cases more robust marker of PM health effects than PM2.5 (3).

54

55

Figure 1. Schematic showing the complexity of sources, atmospheric transformation, and climatic 56

and air quality impacts of particulate Black Carbon (BC).

57

BC measurements have been conducted already since the 1950’s. Yet, no uniform metrics exist 58

for emissions, concentrations or impacts characterization and even the strict definition of BC is 59

missing. BC in atmospheric research and emission studies is characterized by techniques varying 60

in their operation principle (4), producing results of different dimension and metrics. This, together 61

with the lack of universal calibration methods for BC instruments, significantly hinders 62

compilation of consistent BC emission inventories. Furthermore, this complicates the legislative 63

actions for emission mitigation, and the estimation of the effects of BC on global climate and 64

human health.

65

(4)

Several BC control solutions for combustion sources already exist, mainly based on process 66

optimization, fuel choices, flue-gas cleaning and exhaust filtration. A wider implementation of 67

these technologies in developing countries and in the residential sector could further significantly 68

curb the warming (1). Due to the short atmospheric lifetime of BC, the climate benefit from these 69

actions would be immediate. BC mitigation would also produce additional cost savings due to 70

better air quality and consequent health benefits (5).

71

Despite above-mentioned uncertainties and ambiguities in BC measurement, various initiatives to 72

reduce BC emissions have been established by international bodies, such as the Climate and Clean 73

Air Coalition, the Arctic Council’s Arctic Contaminants Action Program (ACAP), International 74

Cryosphere Climate Initiative (ICCI), the UN Convention on Long-range Transboundary Air 75

Pollution and the International Maritime Organization (IMO). Although these examples are mostly 76

voluntary-based non-binding instruments, it is evident that regulations with binding emission 77

reduction targets will come into effect in the future.

78

To improve the communication and start developing a common understanding on BC, there is a 79

clear need to develop simple metrics for BC, i.e., establish a “BC Footprint” concept. BC Footprint 80

would allow to compare different BC emissions sources and levels of atmospheric BC 81

concentrations, and would enable more efficient communication regarding the climate, health and 82

air quality impacts of BC. Practical examples on the use of the BC Footprint concept are numerous.

83

It would for instance, allow comparing the full impacts of the new vehicle technologies. So far, 84

particulate filters installed on diesel and, recently, gasoline vehicles are considered to increase 85

carbon footprint, due to their impact on fuel consumption. However, the simultaneous reduction 86

of BC emissions they offer, and thus the BC Footprint of relevant vehicles, can counter-balance 87

the negative climate impact in the short-term. Another example is residential heating with biomass, 88

(5)

that has zero carbon footprint, but still has BC emissions and climate impacts that are not taken 89

into account when only considering CO2 emissions.

90

In-line with the carbon footprint, the BC Footprint concept can be built on detailed, application- 91

specific BC emission factors from different combustion processes to providing bases for the 92

uniform metrics. It has to overcome the discrepancies due to the measurement methodology, 93

instruments’ features and the sampling techniques utilized. The proposed concept needs to allow 94

calculation of the BC Footprint of certain actions (e.g. producing a megawatt of energy or 95

utilization of solid, liquid and gaseous biofuels), services (e.g. public transportation) or 96

manufacturing of products, thus providing the common grounds for scientific, policy and public 97

communication. Importantly, the BC Footprint should use easily adoptable units to allow the 98

quantification of climatic influences of BC and to compare the emissions.

99

Finally, the BC Footprint would enable simple calculation, visualization and communication of 100

BC emissions and their climate impacts by proving simple metrics for BC. These could be used to 101

demonstrate climate-friendly practices and products to companies’ decision-making procedures, 102

to consumers and, overall, to facilitate the dialogue between the scientific community, companies, 103

political actors, and citizens. We encourage researchers across the world to participate the 104

development of BC Footprint and to adopt the idea into the scientific research and development.

105

106

ACKNOWLEDGMENT 107

We gratefully acknowledge financial support from the Business Finland (4831/31/2018 and 108

4703/31/2018).

109

110

(6)

REFERENCES 111

1. AMAP, 2015. Summary for Policy-makers: Arctic Climate Issues 2015. Arctic Monitoring 112

and Assessment Programme (AMAP), Oslo, Norway. pp. 16.

113

2. Klimont, Z.; Kupiainen, K.; Heyes C.; Purohit P.; Cofala J.; Rafaj P.; Borken-Kleefeld J.;

114

Schöpp W. Global anthropogenic emissions of particulate matter including black carbon.

115

Atmospheric Chemistry and Physics, 2017, 17,8681–8723, DOI 10.5194/acp-17-8681- 116

2017.

117

3. Achilleos, S.; Kioumourtzoglou, M. A.; Wu, C. D.; Schwartz, J. D.; Koutrakis, P.;

118

Papatheodorou, S. I. Acute effects of fine particulate matter constituents on mortality: A 119

systematic review and meta-regression analysis. Environment international, 2017, 109, 120

89-100.

121

4. Bond, T. C.; Doherty, S. J.; Fahey, D. W.; Forster, P. M.; Berntsen, T.; DeAngelo, B. J.;

122

Flanner, M. G.; Ghan, S.; Kärcher, B.; Koch, D.; Kinne, S.; Kondo, Y.; Quinn, P. K.;

123

Sarofim, M. C.; Schultz, M. G.; Schulz, M.; Venkataraman, C.; Zhang, H.; Zhang, S.;

124

Bellouin, N.; Guttikunda, S. K.; Hopke, P. K.; Jacobson, M. Z.; Kaiser, J. W.; Klimont, Z.;

125

Lohmann, U.; Schwarz, J. P.; Shindell, D.; Storelvmo, T.; Warren, S. G.; Zender, C. S.

126

Bounding the role of black carbon in the climate system: A scientific assessment. Journal 127

of Geophysical Research: Atmospheres, 2013, 118, 5380-5552;DOI 10.1002/jgrd.50171, 128

2013.

129

5. Segersson, D.; Eneroth, K.; Gidhagen, L.; Johansson, C.; Omstedt, G.; Nylén, A. E.;

130

Forsberg, B. Health impact of PM10, PM2. 5 and black carbon exposure due to different 131

(7)

source sectors in Stockholm, Gothenburg and Umea, Sweden. International journal of 132

environmental research and public health, 2017, 14 (7), 742.

133

134

Viittaukset

LIITTYVÄT TIEDOSTOT

121 I W Zartman and S Touval, ‘International Mediation: Conflict Resolution and Power Politics’. Journal of Social Issues, vol.. of the political system, and businesses, not only

(2008) Water-soluble organic carbon in urban aerosol: concentrations, size distributions and contribution to particulate matter.. Niemi J.V., Saarikoski S., Tervahattu H., Mäkelä

This is an im- portant result: while the potential in BC emission reductions in the Arctic Council member states may be small compared to the global total, the potential to

Concentrations of fine (PM 2.5 ) and sum of fine and coarse particulate matter (PM 10 ), accumulation mode particle number, black carbon and surface ozone were 4.0, 3.9, 4.5, 6.8

In this study, the chemical composition of ambient fine particulate matter (PM 1 ) was meas- ured at an urban background station for a year in order to determine PM sources

Reducing emissions of black carbon can help to mitigate climate change globally, but particularly in arctic regions... What is

The global or even Arctic-wide climate impacts of black carbon emissions from future Arctic shipping may be reasonably challenged, but the effects of increased Arctic marine

The spectral slope coefficient of chromophoric dissolved organic matter (S275−295) as a tracer of terrigenous dissolved organic carbon in river-influenced ocean margins. Effects