characterizing lignin as an atmospherically long-lived ice ... · 1.sonication: àextraction tool...

1
Lignin’s IN ability: 1. is relevant for mixed-phase clouds à n m from 1 to 10 5 INPs/mg C (– 7 to – 26 °C) 2. is robust and lasts the aerosols’ lifetime à INA decrease to the water background requires harsh laboratory treatments (260 °C, [400:1] mL H 2 O 2 : g lignin) à minimal change through atmospheric processing (exposed to up to 1 ppm O 3 , to up to 25 h of UVB light with an atmospheric equivalent of 6.5 days sunlight) 3. is retained after structural changes in the biopolymer’s chromophoric structure à decrease of UV/Vis absorption (200 – 400 nm) after exposure to UVB light or ozone 1. Sonication: à extraction tool for particulates on aerosol filters, radical reactions may affect chemical structure (Miljevic et al., AS&T, 2014 4 ) 2. Heating: à volatilization of organic material by pyrolysis à experiment: heating of lignin as powder, then H 2 O addition to 200 mg C/L à – INA with + Heating T, FrzT of H 2 O reached after heating to 260 °C à + relative INA after removal of insoluble fraction, as mass loss 3. H 2 O 2 : à oxidative removal of organic material à experiment: reactions with varying ratios of mL H 2 O 2 (35 w%) : g lignin, then dilution with H 2 O to 200 mg C/L à – INA with + ratio of H 2 O 2 to lignin, FrzT of background with H 2 O reached after ratio 400:1 Freezing Ice Nuclei Counter (FINC) (Miller et al., 2020 1 ) à droplet freezing (20 µL, range 0 °C to – 26 °C) à 288 freezing events per experiment Background: à Understanding the ice formation pathways in mixed-phase clouds remains crucial for climate models. à Heterogenous ice formation (> – 38 °C) relies on ice nucleating particles (INPs). à Organic aerosols are ubiquitous and a source of INPs, but their complexity hinders detailed IN ability (INA) characterizations. à The biopolymer lignin is a subcomponent of organic aerosols and serves as proxy for organic matter. Research Questions: By analyzing lignin as an INP we want to contribute to the characterization of INA in organic aerosols. What is lignin’s ability to act as an ice nucleating particle in mixed-phase clouds? What are the effects of... A. typical IN laboratory treatments B. atmospheric processing ... on lignin’s INA? Characterizing lignin as an atmospherically long-lived ice nucleating biopolymer in immersion freezing Sophie Bogler 1 ( @BoglerSophie), Nadine Borduas-Dedekind 1,2 1 Institute for Biogeochemistry and Pollutant Dynamics, ETH Zürich, Zürich, Switzerland 2 Institute for Atmospheric and Climate Science, ETH Zürich, Zürich, Switzerland 3 Lignin’s Ice Nucleating Ability 6 Conclusions 1 Introduction 2 Methods – Ice Nucleation Setup cooling bath camera PCR tray raw data – example image frozen liquid Lignin’s INA is relevant for mixed-phase clouds, but lower than INA of complex dissolved organic matter (DOM) à n m range from 1 to 10 5 INPs/mg C (– 7 °C to – 26 °C) à 50% FF at – 18.7 °C for 200 mg C/L à + relative INA with – concentration, + interactions with water Wilson et al., Nature, 2015 2 water background ( bg ) Borduas et. al, ACP, 2019 3 lignin Acknowledgements: Laboratory assistance: Rachele Ossola, Silvan Müller Funding: SNSF Ambizione Grant and ETH Zürich B. ozonation photochemistry INA decrease no change in INA 4 Laboratory Treatments 1. Ozonation: à experiment: bubbling of 0.1 L/min O 3 (100 ppb – 1 ppm) through bulk solution of 20 mg C/L up to 6.5 h 2. Photochemistry: à experiment: up to 25 h (6.5 days atmospheric equivalent) of UVB irradiation on 20 mg C/L solution à small – trend in lignin’s INA through photochemistry, however less than observed for complex DOM (Borduas et al., ACP, 2019 3 ) à max. – 1 °C decrease at 50% FF after 22 h compared to 0 h Measurement of UV/Vis spectra (200 – 400 nm) à – absorbance after exposure to ozone or UVB irradiation à decay of chromophoric components in lignin’s structure à the IN activity is mostly retained despite this decay, so these chromophores are not decisive for the biopolymer’s INA 5 Atmospheric Processing A. sonication heating H 2 O 2 How does lignin act as INP? Visualization methods: (1) Frozen Fraction (FF) vs Freezing Temp. (FrzT) (2) n m : normalization to carbon content (3) boxplots: mean median 25 th -75 th %ile outliers (<10 th , >90 th %ile) References: minimal INA decrease 1 A. Miller, K. Brennan, C. Mignani, J. Wieder, A. Zapori, and Nadine Borduas-Dedekind, 2020, manuscript in preparation 2 T. W. Wilson, L. A. Ladino, P. A. Alpert, M. N. Breckels, I. M. Brooks, J. Browse, S. M. Burrows, K. S. Carslaw, J. A. Huffman, C. Juddand et al, Nature, 2015, 525, 234–238. 3 N. Borduas-Dedekind, R. Ossola, R. O. David, L. S. Boynton, V. Weichlinger, Z. A. Kanji and K. McNeill, Atmospheric Chemistry and Physics Discussions, 2019, 1–27. 4 B. Miljevic, F. Hedayat, S. Stevanovic, K. E. Fairfull-Smith, S. E. Bottle and Z. D. Ristovski, Aerosol Science and Technology, 2014, 48, 1276–1284. INA decrease no change in INA data analysis inactive active lignin heat

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Page 1: Characterizing lignin as an atmospherically long-lived ice ... · 1.Sonication: àextraction tool for particulates on aerosol filters, radical reactions may affect chemical structure

Partners

Lignin’s IN ability:1. is relevant for mixed-phase cloudsà nm from 1 to 105 INPs/mg C (– 7 to – 26 °C)2. is robust and lasts the aerosols’ lifetimeà INA decrease to the water background requires harsh laboratory treatments (≧ 260 °C,

[400:1] mL H2O2 : g lignin)

à minimal change through atmospheric processing (exposed to up to 1 ppm O3, to up to 25 h of UVB light with an atmospheric equivalent of 6.5 days sunlight)

3. is retained after structural changes in the biopolymer’s chromophoricstructureà decrease of UV/Vis absorption (200 – 400 nm) after exposure to UVB light or ozone

1. Sonication:à extraction tool for particulates on aerosol filters, radical reactions may affect chemical

structure (Miljevic et al., AS&T, 20144)

2. Heating:à volatilization of organic material by

pyrolysisà experiment: heating of lignin as powder,

then H2O addition to 200 mg C/Là – INA with + Heating T, FrzT of H2O

reached after heating to 260 °Cà + relative INA after removal of insoluble

fraction, as mass loss

3. H2O2:à oxidative removal of organic materialà experiment: reactions with varying

ratios of mL H2O2 (35 w%) : g lignin, then dilution with H2O to 200 mg C/L

à – INA with + ratio of H2O2 to lignin,FrzT of background with H2O reachedafter ratio 400:1

Freezing Ice Nuclei Counter (FINC) (Miller et al., 20201)à droplet freezing (20 µL, range 0 °C to – 26 °C)à 288 freezing events per experiment

Background:à Understanding the ice formation pathways in

mixed-phase clouds remains crucial for climate models.

à Heterogenous ice formation (> – 38 °C) relies on ice nucleating particles (INPs).

à Organic aerosols are ubiquitous and a source of INPs, but their complexity hinders detailed IN ability (INA) characterizations.

à The biopolymer lignin is a subcomponent of organic aerosols and serves as proxy for organic matter.

Research Questions:By analyzing lignin as an INP we want to contribute to the characterization of INA in organic aerosols.

What is lignin’s ability to act as an ice nucleating particle in mixed-phase clouds?

What are the effects of...A. typical IN laboratory treatmentsB. atmospheric processing... on lignin’s INA?

Characterizing lignin as an atmospherically long-lived ice nucleating biopolymer in immersion freezingSophie Bogler1 ( @BoglerSophie), Nadine Borduas-Dedekind1,2 1Institute for Biogeochemistry and Pollutant Dynamics, ETH Zürich, Zürich, Switzerland2Institute for Atmospheric and Climate Science, ETH Zürich, Zürich, Switzerland

3 Lignin’s Ice Nucleating Ability

6 Conclusions

1 Introduction

2 Methods – Ice Nucleation Setup

cooling bath

camera

PCRtray

raw data –example image

frozen liquid

Lignin’s INA is relevant for mixed-phase clouds, but lower than INA of complexdissolved organic matter (DOM)à nm range from 1 to 105 INPs/mg C (– 7 °C to – 26 °C)à 50% FF at – 18.7 °C for 200 mg C/Là + relative INA with – concentration, + interactions with water

Wilson et al., Nature, 2015 2

water background (bg)

Borduaset. al,

ACP, 2019 3

lignin

Acknowledgements: Laboratory assistance: Rachele Ossola, Silvan MüllerFunding: SNSF Ambizione Grant and ETH Zürich

B. ozonationphotochemistry

INA decrease

no change in INA

4 Laboratory Treatments1. Ozonation:à experiment: bubbling of 0.1 L/min O3 (100 ppb – 1 ppm) through bulk solution of

20 mg C/L up to 6.5 h

2. Photochemistry:à experiment: up to 25 h (6.5 days atmospheric equivalent) of UVB irradiation on

20 mg C/L solutionà small – trend in lignin’s INA through photochemistry, however less than observed for

complex DOM (Borduas et al., ACP, 20193)à max. – 1 °C decrease at 50% FF after 22 h compared to 0 h

Measurement ofUV/Vis spectra(200 – 400 nm)à – absorbance after

exposure to ozone or UVB irradiation

à decay of chromophoriccomponents in lignin’s structure

à the IN activity is mostlyretained despite this decay, so these chromophoresare not decisive for the biopolymer’s INA

5 Atmospheric Processing

A. sonication heatingH2O2

How does lignin

act as INP?

Visualization methods:(1) Frozen Fraction (FF) vs Freezing Temp. (FrzT)(2) nm: normalization to carbon content(3) boxplots: mean

median25th-75th %ile

outliers (<10th, >90th %ile)

References:

minimal INA decrease

1 A. Miller, K. Brennan, C. Mignani, J. Wieder, A. Zapori, and Nadine Borduas-Dedekind, 2020, manuscript in preparation2 T. W. Wilson, L. A. Ladino, P. A. Alpert, M. N. Breckels, I. M. Brooks, J. Browse, S. M. Burrows, K. S. Carslaw, J. A. Huffman, C. Judd and et al, Nature, 2015, 525, 234–238.3 N. Borduas-Dedekind, R. Ossola, R. O. David, L. S. Boynton, V. Weichlinger, Z. A. Kanji and K. McNeill, Atmospheric Chemistry and Physics Discussions, 2019, 1–27.4 B. Miljevic, F. Hedayat, S. Stevanovic, K. E. Fairfull-Smith, S. E. Bottle and Z. D. Ristovski, Aerosol Science and Technology, 2014, 48, 1276–1284.

INA decrease

no change in INA

data analysis

inactive

active

lignin

heat

INA

mass

surface

decrease

no change

no change

no change

decrease

increase