19th century glacier retreat in the Alps preceded the emergence of industrial black carbon deposition on high-alpine glaciers
- 1Laboratory of Environmental Chemistry, Paul Scherrer Institut, 5232 Villigen, Switzerland
- 2Oeschger Centre for Climate Change Research, University of Bern, 3012 Bern, Switzerland
- 3Research School of Earth Sciences and the ARC Centre of Excellence for Climate System Science, Australian National University, Canberra 2601 ACT, Australia
- 4Institute for the Dynamics of the Environmental Sciences, National Research Council (IDPA-CNR), 30172 Venice, Italy
- 5Department of Chemistry and Biochemistry, University of Bern, 3012 Bern, Switzerland
Correspondence: Michael Sigl (firstname.lastname@example.org)
Light absorbing aerosols in the atmosphere and cryosphere play an important role in the climate system. Their presence in ambient air and snow changes the radiative properties of these systems, thus contributing to increased atmospheric warming and snowmelt. High spatio-temporal variability of aerosol concentrations and a shortage of long-term observations contribute to large uncertainties in properly assigning the climate effects of aerosols through time.
Starting around AD 1860, many glaciers in the European Alps began to retreat from their maximum mid-19th century terminus positions, thereby visualizing the end of the Little Ice Age in Europe. Radiative forcing by increasing deposition of industrial black carbon to snow has been suggested as the main driver of the abrupt glacier retreats in the Alps. The basis for this hypothesis was model simulations using elemental carbon concentrations at low temporal resolution from two ice cores in the Alps.
Here we present sub-annually resolved concentration records of refractory black carbon (rBC; using soot photometry) as well as distinctive tracers for mineral dust, biomass burning and industrial pollution from the Colle Gnifetti ice core in the Alps from AD 1741 to 2015. These records allow precise assessment of a potential relation between the timing of observed acceleration of glacier melt in the mid-19th century with an increase of rBC deposition on the glacier caused by the industrialization of Western Europe. Our study reveals that in AD 1875, the time when rBC ice-core concentrations started to significantly increase, the majority of Alpine glaciers had already experienced more than 80 % of their total 19th century length reduction, casting doubt on a leading role for soot in terminating of the Little Ice Age. Attribution of glacial retreat requires expansion of the spatial network and sampling density of high alpine ice cores to balance potential biasing effects arising from transport, deposition, and snow conservation in individual ice-core records.
The role of aerosols in climate forcing (defined as perturbation of the Earth's energy balance relative to the pre-industrial) is significant but poorly understood (Charlson et al., 1992). Aerosol emissions and their atmospheric burden vary in time and from region to region; some aerosols cause cooling while even co-emitted species can lead to simultaneous warming. This results in large uncertainties of the ascribed radiative forcing terms to short-lived aerosols in contrast to greenhouse gas forcing (Bond et al., 2013; Dubovik et al., 2002).
Black carbon (BC) has a unique and important role in the climate system because it absorbs solar radiation even at very low concentrations, influences cloud formation, and enhances the melting of snow and ice via albedo feedbacks (Flanner et al., 2007; Hansen and Nazarenko, 2004). BC is defined as an incomplete combustion product from natural biomass burning (e.g. forest fires) or anthropogenic biofuel and fossil-fuel burning. It is insoluble, refractory, strongly absorbs visible light, and forms aggregates of small carbon spherules. Per unit mass, BC has the highest light absorption of all abundant aerosols in the atmosphere (Bond et al., 2013). Given that carbonaceous aerosols in the atmosphere present a continuum of varying physical and chemical properties, their quantification is strongly related to the analytical method used. A wide range of terminologies has developed in the scientific community to characterize BC and related carbonaceous aerosols, and we follow the terminology recommendations recently put in place (Petzold et al., 2013). Refractory black carbon (rBC) will be used instead of black carbon for reporting concentrations derived from our laser-based incandescence method, while the general term black carbon (BC) is used for a qualitative description when referring to light-absorbing carbonaceous substances in atmospheric aerosol. If analysed with a thermal optical method, BC is also referred to as elemental carbon (EC) (Currie et al., 2002).
While natural sources such as forest fires dominated the global BC burden in the pre-industrial atmosphere, current emissions are largely driven by industrial, energy related sources (Bond et al., 2013). The modern burden is highest in heavily industrialized and populated regions including China, India, and Europe (Fig. 1). Trends in BC emissions estimated from bottom-up approaches (i.e. from fuel consumption data) suggest large changes during the industrial era (Bond et al., 2007; Lamarque et al., 2010), which were recently largely confirmed by continuous measurements of BC in Greenland ice cores (Bauer et al., 2013; Koch et al., 2011; Y. H. Lee et al., 2013; McConnell et al., 2007). However, multiple source regions contribute in varying degrees to the BC deposition over Greenland, hampering attribution of the observed trends to individual emission source areas (Hirdman et al., 2010; Liu et al., 2011).
Together with mineral dust and other absorbing organic aerosols, BC deposited on snow and ice can lead to increased melt rates and changes in melt onset due to reductions in surface albedo. These effects are further enhanced by subsequent snow albedo feedbacks such as an increase in the water content and surface accumulation of impurities (Flanner et al., 2009; Hansen and Nazarenko, 2004). The best estimate for industrial era global forcing of BC is +0.13 W m−2, but values for regions with seasonal snow cover (e.g. the Arctic, European Alps, Tibetan Plateau) are much higher (Bond et al., 2013). Industrial BC deposition has been suggested as being responsible for observed Arctic warming in the 1940s and recent years (Flanner, 2013; Flanner et al., 2009; Quinn et al., 2008) but recent surface albedo decreases (i.e. darkening) of the Greenland ice sheet occurred in the face of a widespread decrease in BC deposition based on multiple ice cores (Keegan et al., 2014; McConnell et al., 2007), suggesting a small role for light absorbing impurities in causing these changes (Polashenski et al., 2015). In the Himalayas the combined increased deposition of mineral dust and industrial black carbon was suggested to play a role in the observed glacier retreat during the past decades (Flanner and Zender, 2005; Kaspari et al., 2011; Lau et al., 2010; W. S. Lee et al., 2013). In contrast to climate effects from direct radiative forcing (Bond and Sun, 2005; Penner et al., 1998) and cloud effects (Haywood and Boucher, 2000; Lohmann and Feichter, 2005) that are short lived and effective only during the brief atmospheric lifetime of the aerosols (from days to a week), BC-induced changes in the snow cover persist for longer periods of time ranging from weeks-to-months. They are most pronounced during the spring and summer, when insolation and seasonal snowmelt reach a maximum (Flanner et al., 2009).
To quantify trends and magnitudes of climate forcing from BC in the atmosphere (direct and indirect effect) and cryosphere (snow-albedo effect) climate-model simulations are widely used (Bond et al., 2013; Lamarque et al., 2013; Shindell et al., 2013). These rely strongly on energy-consumption based estimates of BC emissions that are highly uncertain (see Fig. 8 in Bond et al., 2007) and thus need to be evaluated against independent ice-core based observations (Bauer et al., 2013; Y. H. Lee et al., 2013). Those comparisons allow identification of mismatches and can subsequently help to improve parameterization and model performance (Lamarque et al., 2013).
Mountain glaciers are retreating worldwide and are projected to further shrink with the expected increase in global surface temperatures due to increasing greenhouse gas concentrations (Mernild et al., 2013; Oerlemans, 2005; Zemp et al., 2006). While the currently observed mass loss is global in scale and attributed to anthropogenic greenhouse gas emissions, the onset of melting during the 19th century was asynchronous for many mountain regions (e.g. between Scandinavia and the Alps; Imhof et al., 2012; Larsen et al., 2013). Observations place the start of the retreat in the Western Alps from 1860 to 1865 after glaciers reached their maximum extent around 1850–1855 (Nussbaumer and Zumbühl, 2012; Zumbühl et al., 2008). The retreat was rapid and synchronous among different documented glaciers. By 1880, glacier tongues had retreated by several hundred metres in length (Nussbaumer and Zumbühl, 2012). Using early instrumental temperature and precipitation data, a combination of high spring temperatures and reduced autumn precipitation was suggested as the main drivers of the observed glacier retreat (Steiner et al., 2008; Zumbühl et al., 2008). In an alternative hypothesis, early industrial BC deposited on snow and ice of Alpine glaciers was held responsible for the rapid melting, involving a snow-albedo feedback (Painter et al., 2013). This hypothesis built on model simulations to estimate snow albedo forcing from two ice-core based reconstructions of BC (i.e. EC) from Fiescherhorn glacier (Jenk et al., 2006) and Colle Gnifetti (Thevenon et al., 2009). Starting in the 1870s, both records show an initial 2–3-fold increase of BC concentrations rising from a mostly natural background of 9 ng g−1 to more than 20 ng g−1, before the highest values (37 ng g−1) were reached during the early 20th century.
Transient changes in external natural (e.g. volcanic eruptions) and anthropogenic climate forcing (e.g. greenhouse gases, tropospheric aerosols) occurred during the emergence of industrialization in Europe (Eyring et al., 2016; Jungclaus et al., 2017). To isolate the often complex relationships between glacier fluctuations and meteorological forcing and to identify the mechanisms responsible for glacier retreat in the second half of the 19th century requires comprehensive modelling efforts (e.g. Lüthi, 2014; Zekollari, 2017; Goosse et al., 2018). Underpinning such efforts, accurate and precise delineation of external forcing (e.g. volcanic eruptions), potential feedbacks (e.g. BC deposition on snow) and cryosphere changes (e.g. variations in glacier front positions) is critically important.
The snow-albedo feedback hypothesis formulated by Painter et al. (2013) was a first effort to attempt this but was limited predominantly by the available BC data at that time (Thevenon et al., 2009; Jenk et al., 2006). The available data were of relatively low time-resolution (Thevenon et al., 2009; Jenk et al., 2006), and the dating of the Colle Gnifetti ice core was at that time not based on annual-layer dating constrained by historic age markers (Jenk et al., 2009; see Fig. S1 and Table S1 in the Supplement) and thus was highly uncertain in Thevenon et al. (2009). Measurements of EC may be subject to artifacts related to losses during filtration, interferences from mineral dust, or the pyrolysis of organic compounds (see Lack et al., 2014; Lim et al., 2014, for details). Large sample size requirements (0.2–1 kg) for EC quantification with traditional thermal techniques, however, made it impossible to analyse replicate core sections in order to demonstrate the repeatability of the results (Thevenon et al., 2009; Jenk et al., 2006).
Here, we set out to re-evaluate the timing of industrial BC deposition in ice cores from the Alps by using a new, more accurately dated record of rBC at a much higher time resolution (sub-annual). In addition, we measure distinctive tracers of anthropogenic pollution (e.g. bismuth, sulfate, lead, ammonium) and compare all records with the most highly resolved history of glacier length changes of four glaciers in the Western Alps currently available (Nussbaumer and Zumbühl 2012).
2.1 Ice-core drilling site
Two 82 m long ice cores (CG03A, CG03B) from the European Alps, which are surrounded by highly industrialized countries (e.g. Germany, Italy, France), representing some of the main emitters of 19th to 21st century fossil-fuel industrial BC (Bond et al., 2007), were drilled in 2003 a metre apart on Colle Gnifetti (Monte Rosa, 4450 m a.s.l., 45∘55′55 N; 07∘52′34 E, Jenk et al., 2009) (Fig. 1). The drill site location on a saddle minimizes effects of lateral ice flow, but leads to seasonally weighted atmospheric signals, due to preferential wind erosion of winter snow (Bohleber et al., 2013; Häberli et al., 1983; Oeschger, 1977; Schwikowski et al., 1999a). Low annual net accumulation rates (0.45 m w.e. yr−1) give access to an older level of ice and allow the retrieval of long-term proxy records covering most of the Holocene (Jenk et al., 2009; Konrad et al., 2013; Sigl et al., 2009). During the summer months, the drill site is frequently situated above the planetary boundary layer. However, the site clearly records the signal of natural and anthropogenic emissions from sources located at lower altitudes, as indicated by the diurnal and annual cycle of aerosol deposition resulting from convective transport monitored in situ at Colle Gnifetti and Jungfraujoch over many years by remote sensing and high-resolution aerosol measurements (Lugauer et al., 1998; Nyeki et al., 2000). The presence of these annual cycles is the basis for the dating of these ice cores by incremental layer-counting reaching as far back as 1000 years (Bohleber et al., 2018). On inter-annual timescales, the summer-biased and irregular snow deposition at Colle Gnifetti contributes to the observed variability of the proxy records, with occasionally preserved winter snowfall (e.g. in ∼AD 1890) typically having low impurity concentrations (Wagenbach et al., 2012). However, these effects are minimized at a (multi-) decadal resolution, at which these proxy records reflect changes in the source strengths of the emissions and the resulting atmospheric burden of aerosols remarkably well (Engardt et al., 2017; Fagerli et al., 2007; Gabrieli et al., 2010; Schwikowski et al., 1999b). Additional firn and ice cores (CG08, CG15) were obtained from the same site in 2008 (Kirchgeorg et al., 2013) and in September 2015, respectively, to update the long-term record to the most recent past.
The Colle Gnifetti site has produced a number of impurity and pollution records, highlighting the strong impact of human activity on the atmospheric composition over Central Europe during recent decades and centuries, including records of sulfate and nitrate (Döscher et al., 1995; Schwikowski et al., 1999a), ammonium (Döscher et al., 1996), carbonaceous aerosols (Lavanchy et al., 1999; Thevenon et al., 2009), trace elements such as lead, copper, cadmium, zinc, plutonium (Barbante et al., 2004; Gabrieli and Barbante, 2014; Gabrieli et al., 2011; Schwikowski et al., 2004), and organic pollutants (Gabrieli et al., 2010; Kirchgeorg et al., 2013). Temporal variability of mineral dust, including long-range transported dust from Africa, was investigated by Bohleber et al. (2018), Gabbi et al. (2015), Gabrieli and Barbante (2014), Wagenbach and Geis (1989), and Wagenbach et al. (1996) using calcium, sulfate, iron, and barium as mineral dust proxies.
2.2 Analytical methods
The top 57.2 m of CG03B comprising 1635 discrete samples (cross section area 1.9×1.9 cm) were analysed at the Paul Scherrer Institut (PSI) between May and July 2015 (Table 1) achieving sub-annual resolution since the pre-industrial (i.e. AD 1741). Concentrations of rBC were determined with a Single Particle Soot Photometer (SP2, Droplet Measurement Technologies, Schwarz et al., 2006) and a jet (APEX-Q, Elemental Scientific Inc.) nebulizer to aerosolize the aqueous samples (Wendl et al., 2014). BC analysis was done at approximately 2 cm water equivalent depth resolution. Freshly cut samples stored in polypropylene vials were melted at room temperatures, sonicated for 25 min and measured immediately using an auto-sampler (CETAC ASX-520). Liquid sample flow rates typically varying within ±10 % were measured routinely to ensure constant aerosolization efficiencies. Capillaries delivering samples to the nebulizer were rinsed at least on a daily basis with 3 % nitric acid for 10 min. For external calibration we used rBC standard solutions (Aquadag®, Acheson Inc.; see Wendl et al., 2014, for details) freshly prepared and directly analysed at concentrations from 0.1 to 50 ng g−1. To demonstrate the reproducibility of the rBC measurements and the robustness of the method we performed 387 replication analyses using parallel ice-core sections that comprised 20 % of the length of the original analyses. The upper 11.9 m of CG15, in total 276 samples, were similarly analysed. Following rBC analyses, we determined the concentrations of major ions (Na+, , K+, Ca2+, Mg2+, Cl−, , ) using ion-chromatography (850 Professional IC, Metrohm).
For the parallel ice core CG03A a wide range of additional elemental and chemical components of aerosols had been analysed using ion-chromatography (IC, Dionex) and inductively coupled plasma mass spectrometry (ICPMS, Agilent 7500), enabling ice-core dating (Jenk et al., 2009) and detailed characterization of dust and pollution aerosols (Gabrieli and Barbante, 2014). Trace element analyses were performed at University of Venice using the ICPMS in continuous flow mode, achieving an effective sampling resolution of approximately 0.5 cm water equivalent (Gabrieli and Barbante, 2014). Here we present measurements of trace metals (i.e. bismuth, Bi), typically emitted by coal burning and other industrial processes (McConnell and Edwards, 2008) and of chemical tracers (i.e. calcium, Ca2+) typically enriched in mineral dust originating predominantly from the Saharan deserts and constituting a second potential source for light-adsorbing impurities present in Alpine glacier ice.
2.3 Ice-core dating
The CG03B ice core was dated against the chronology of the CG03A core (Jenk et al., 2009) using the major ion records obtained for both cores to align the records. In total, 221 stratigraphic links were established between these two records between AD 1741 and 2003, which is close to the number of annual layers identified originally in CG03A. Linear interpolation was used to date the ice between the stratigraphic tie-points. Differences in the depths for common time markers are found to be less than 13 cm at most (Table S1). The chronology of CG03A (Fig. S1; Table S1) was originally derived by annual-layer-counting predominantly using the record and constrained by absolute age markers from volcanic eruptions, nuclear weapon testing, historic Saharan dust events and 14C dating of insoluble organic carbon in the deeper core sections (Jenk et al., 2009; Sigl et al., 2009; Uglietti et al., 2016). Previously identified volcanic horizons (i.e. Katmai, 1912; Tambora, 1815; Laki, 1783) were corroborated in the new CG03B records using concentrations together with the ratio of . Additional volcanic signatures (e.g. in 1809) potentially relating to a large eruption of unknown origin in AD 1809 were detected in CG03B but have not been used to further constrain the timescale. Constrained by historic events during the beginning and end of the 19th century, maximum age uncertainties are conservatively estimated to be ±5 years at most during the mid-19th century (Jenk et al., 2009).
2.4 BC emission inventories
In the absence of direct BC measurements during the last few centuries, gridded emission inventories from bottom-up approaches, (e.g. Bond et al., 2007; Lamarque et al., 2010) are widely used to estimate emissions and aerosol loading. These are the final products of a wide range of estimates of activity (e.g. fuel consumption) combined with emission factors (e.g. grams of BC emitted per mass of fuel burned derived from controlled burning of fuel types under laboratory conditions) and thus carry large uncertainties (Bond et al., 2013). While the general emission trends from these inventories could be confirmed through comparison to existing ice-core reconstructions (Jenk et al., 2006; Junker and Liousse, 2008; Lavanchy et al., 1999), a more detailed evaluation was hampered by the relatively large error ranges inherent in both these reconstruction approaches. For this study, we deploy the BC emission estimates from fossil-fuel and biofuel burning (available at 5-year resolution) from Bond et al. (2007), for (1) the OECD countries in Europe and (2) the mean of the grid cells 45–47∘ N and 6–9∘ E (available at 10-year resolution) that encompasses both, our ice-core study site and the locations of various glacier length reconstructions in the Western Alps (see Sect. 2.5; Fig. 1).
2.5 High-resolution glacier length histories from Western Alps
Glacier fluctuations in the European Alps are among the best documented worldwide, as glaciers are situated in densely populated areas. Painter et al. (2013) used five glaciers from the Western and Eastern Alps to analyse the 19th century changes of their terminus positions, with Unterer Grindelwald glacier providing the densest observation frequency during the 19th century among these glaciers. For this study, we compile four glacier length reconstructions from the Western Alps (all situated in close proximity to the ice-core site) including Mer de Glace, Oberer Grindelwald and Unterer Grindelwald glacier, and Bossons glacier (Nussbaumer and Zumbühl, 2012), the latter offering the highest observation density during the mid-to-late 19th century with annual data coverage between AD 1850 and 1899 of 78 %. To analyse trends in glacier length variability relative to the increase of industrial black carbon deposition at Colle Gnifetti and Fiescherhorn (Jenk et al., 2006), we filled missing terminus position data by linear interpolation and constructed a stacked glacier length curve by averaging the terminus positions of all four glaciers.
2.6 Time-of-emergence (ToE) analyses
To determine the timing when rBC concentrations exceeded their natural variability, suggesting an additional, industrial emission source, we performed a time-of-emergence (ToE) analysis on annually averaged rBC concentrations. The ToE is formally defined by Hawkins and Sutton (2012) as the mean time at which the signal of change emerges from the noise of natural variability. We followed the methods of Abram et al. (2016) in defining the threshold of emergence value as the earliest occurrence where the signal-to-noise ratio exceeds the value 2 (industrial rBC signal is distinguishable from zero at a 95 % confidence level). We consider the time period AD 1741 to 1840 as the pre-industrial reference period during which human emissions of light absorbing rBC in Central Europe was minimal, restricted to occasional forest fires and residential wood burning (henceforth summarized as biomass burning BB). To discriminate large rBC values caused by BB within the pre-industrial period (AD 1741–1850) we employed a fire detection algorithm adapted from Fischer et al. (2015) and replaced the correspondent BC concentration values for detected “fire activity” years with their 11-year running medians (BCno BB). The ToE assessment was carried out varying the length of the pre-industrial reference period and the degree of smoothing (running mean) applied to the record to determine the underlying signal. Reference periods from 15 to 100 years in length were used beginning in 1741 (i.e. shortest reference period is AD 1741–1765 and longest reference period is AD 1741–1840) were used to determine the mean and +2σ level of natural variability. A running mean of the same length as used for the reference period was applied to determine the signal and ToE was assigned to the year when the signal first permanently exceeded the +2σ value of the reference period. This method results in a distribution of ToE estimates that reflect uncertainty based on methodological choices in defining the signal and noise values used to define ToE. We assume the uncertainty in ToE to be independent from the ice-core dating uncertainty, and use their root sum square as the total uncertainty estimate of the emergence of enhanced industrial BC emissions. ToE analysis was similarly applied to total rBC (without discriminating BB years) and to Ca2+ as a proxy for Saharan dust deposition, the latter having also high abundances of light-absorbing minerals such as hematite Fe2O3 (Linke et al., 2006). To evaluate the sensitivity of the choice of detection method for ToE we also employed a Bayesian change-point algorithm (Ruggieri, 2013) based on a linear regression model to determine the timing for a significant change point (equivalent to the emergence) within the rBC time series.
3.1 BC and source tracer variability since AD 1741
The synchronized records of CG03, CG08 and CG15 (Fig. S2) provide a continuous record of long-term changes of rBC deposition at this site from the pre-industrial (AD 1741) into the most recent past (AD 2015, Fig. 2). Deposition histories for major aerosol species are highly reproducible in the two parallel CG03 ice cores (Figs. S3, S4), indicating minimal adverse effects of snow drift and spatial variability of aerosol deposition present at these spatial scales. Measured rBC values at CG03B vary strongly on intra-annual timescales, with this variability being superimposed on longer-term trends. Replicate analyses performed at the end of the measurement campaign confirm that the original measurements performed over 2 months are highly reproducible over a concentration range of almost 3 orders of magnitude (Figs. 2, S5). Between 1975 and 2015 (N>12 samples per year) the highest values of >15 ng g−1 (90 percentile) are typically recorded during the summer months, reflecting increased deposition of aerosol species on the glacier during times when the planetary boundary layer reaches higher than the drilling site at 4450 m (Lugauer et al., 1998). During the remaining season of snow accumulation, the ice-core site is situated within the free troposphere with rBC concentrations significantly lower with approximately 0.9 ng g−1 (10 percentile). Due to common transport and deposition, co-variability of rBC with other species at intra-annual resolution is indicated by significant Pearson's correlation coefficients (p<0.001, one sided, N=696, Na+, R=0.35; , R=0.63) for the period of the most recent 40 years.
All concentrations are median concentrations in ng g−1, except Bi (pg g−1); calcium, sulfate, sodium and nitrate values are the mean from both ice cores CG03A and CG03B. BC is from CG03B, all others are from CG03A. cb: coal burning; ind: industrial; t: traffic; bb: biomass burning; ff: forest fires; a: agriculture; b: biogenic; ss: sea salt; d: mineral dust; vol: volcano.
To analyse long-term rBC variability we calculate annual mean values by averaging all rBC values within the respective calendar year (Fig. 3). Excluding occasional rBC spikes (>4 ng g−1) the mean rBC concentration in the CG03 core during the pre-industrial (i.e. AD 1741–1850) was 2 ng g−1, followed by a small (2-fold) increase to approximately 4 ng g−1 during the last two decades of the 19th century (AD 1880–1899). Maximum rBC concentrations of 10 ng g−1 exceeding 5 times the pre-industrial values are recorded between 1910 and 1920 and again 1933–1945, with a short decline between 1921 and 1932 (6 ng g−1), plausibly explained by a drop in industrial rBC emissions following the economic crisis between the two world wars. Since 1950, rBC concentrations remained elevated and only started to drop significantly after AD 2000. Since then, concentrations vary around 5 ng g−1, still more than twice as high as during the pre-industrial period. We summarize median rBC concentrations in Table 2 together with other relevant ice-core source tracers and their main emission sources for the pre-industrial and for two periods labelled after their main fossil-fuel source as coal “COAL” (1901–1950) and petroleum products “PETROLEUM” (1951–1993), respectively. AD 1993 marks the end of the time period for which continuous trace element analyses were performed.
In the pre-industrial period, ammonium (R=0.75, p<0.0001) and nitrate (not shown) are strongly correlated with rBC, indicating that BC was associated with (natural or anthropogenic) biomass burning emissions (Figs. 4 and S6). Sulfate () concentrations started to rise in AD 1900, with this timing well constrained by the Saharan dust event of AD 1901 (Oeschger, 1977; Wagenbach and Geis, 1989). Throughout the COAL era concentrations are strongly correlated with rBC, with this correlation becoming weaker during the PETROLEUM era. Heavy metals such as lead (Pb) and Bi show high relative enrichments, comparable to rBC in particular, from AD 1910 to 1950 indicating an increased association of BC with anthropogenic fossil-fuel emissions (e.g. coal burning) during that time (Table 2). None of the four discussed industrial pollution tracers (rBC, , Pb, Bi) show pronounced increases in concentrations starting in the mid-19th century. In agreement with other dust records from Colle Gnifetti (Bohleber et al., 2018; Wagenbach and Geis, 1989), we observe no enhanced mean (or frequency) of mineral dust deposition throughout the 19th century (Figs. S1, S4). Only during the past three decades (AD 1975–2015), does the dust activity appear to be anomalously high with respect to the long-term variability (Figs. S6), which is thought to relate to increased drought conditions in the main dust source regions in northern Africa (Moulin and Chiapello, 2006).
3.2 Comparison to other ice-core BC records
Few other ice-core records contain precisely dated information about Central European industrial BC emissions for the 19th century. Previous determinations of EC concentrations from the Colle Gnifetti ice core with various methods are characterized by coarse resolution and unknown reproducibility (Lavanchy et al., 1999; Thevenon et al., 2009). The Fiescherhorn FH02 ice core obtained 70 km north of CG03 in the Bernese Alps (3900 m a.s.l., 46∘33′03 N; 08∘04′00 E) provides total EC concentrations from AD 1650 to 1940 at 5–10-year resolution (Fig. 3b) (Jenk et al., 2006) and analyses were recently completed at annual resolution until AD 2002 (Cao et al., 2013; Gabbi et al., 2015). The low-resolution record from Fiescherhorn (Jenk et al., 2006) and Colle Gnifetti (Thevenon et al., 2009) were used by Painter et al. (2013) as input for their model study on potential changes of 19th century snow albedo (note that in Fig. 2 in Painter et al., 2013, the labelling of the two cores was swapped). Despite the coarse resolution, the overall EC trend from Fiescherhorn ice core is closely reproduced by the new rBC record from CG03 (R=0.71, p<0.005) (Fig. 3c, d). Differences in absolute concentrations by approximately a factor of four can be understood to reflect a difference in elevation (FH02 is situated 500 m lower in elevation and closer to the emission sources) and a difference in the analytical methods employed, with thermo-optical methods resulting in consistently higher values compared to photometric determination of rBC (Currie et al., 2002; Lim et al., 2014) (also see Sect. 4.1). Nevertheless, the common three-step increase of concentrations occurring around AD 1875, 1900, and 1940, strongly supports the interpretation that both ice cores capture a common signal of industrial BC emissions increase driven by technological and economic developments in Central Europe. In contrast, the low-resolution EC record of Thevenon et al. (2009) – characterized by varying time resolution and without demonstrated repeatability of the results – shows a markedly different variation in time. As the age-model used by Thevenon et al. (2009) was not forced to intersect with the absolute dated reference horizons, it is biased from the annual-layer dated chronology by, on average, 14 years (7–18 years) during the 19th century (Fig. S7). The final chronology dates the early ∼AD 1850 increase in EC in the 1830s, which would imply an early start of industrialization. This is neither consistent with the new rBC record from Colle Gnifetti or with the Fiescherhorn EC record nor with rBC records from Greenland (see below). Given that mean 16th century EC concentrations reach comparable levels during the peak industrial era of the 20th century, we speculate that the Thevenon et al. (2009) EC record suffered from methodological biases, probably related to the presence of mineral dust (i.e. high EC concentrations occurred often in samples with high dust concentrations, see Fig. 3 in Thevenon et al., 2009).
The non-BB rBC record (CG03 rBCno BB) was compared to an equivalent stacked rBCno BB record obtained from four ice cores (Summit 2010, D4, NEEM-2011-S1, TUNU2013; Fig. 5) from Greenland (Keegan et al., 2014; McConnell et al., 2007; Mernild et al., 2015; Sigl et al., 2013, 2015) acknowledging that these Greenland ice cores capture a mixture of emissions from both northern America and Europe (Bauer et al., 2013; Hirdman et al., 2010; Lamarque et al., 2013; McConnell et al., 2018). Due to high snow accumulation rates and analysed at high-resolution, absolute dating uncertainties for these records are estimated to be better than ±1 year, which provides us with another independent, high-precision age constraint for the onset of increased industrial BC emissions from Europe.
Whereas absolute concentrations are, depending on the specific industrial pollutant (BC, Bi), a factor of 2–4 lower in Greenland, the long-term trends are remarkably similar between the Greenland stack and CG03 (Figs. 4d, 5). Overall, concentrations of major industrial pollutants appeared to have increased earlier by roughly 10 years (in AD 1890) in Greenland compared to the Alps, most prominently visible in bismuth. This delay is consistent with industrialization having accelerated earlier in North America (McConnell and Edwards, 2008) than in the major Central European countries (e.g. Germany, Italy, France). The maximum in industrial BC emissions were synchronous between Greenland and the Alps, both peaking at approximately AD 1915. Differences exist in the long-term trends of rBC since the early 20th century maximum, with Greenland values closely approaching pre-industrial levels while remaining elevated in the Alps.
3.3 Comparison with BC emission inventories
We compare our ice-core based deposition history with estimated emissions of BC from fossil-fuel and bio-fuel burning (Bond et al., 2007) which form the main input for simulating BC climate effects (direct, indirect aerosol, and ice-albedo forcing) on past climate (Flanner et al., 2007; Lamarque et al., 2013; Shindell et al., 2013). We notice that the general structure of BC and EC from the two Alpine ice cores closely resembles estimated BC emissions for both OECD Europe and the western Alpine region taken from the bottom-up inventory of Bond et al. (2007) (Fig. 6). Interpreting the ice-core long-term trends as proxies for atmospheric burden (or emissions, respectively) we identify three major differences between these datasets. First, the increase in BC to its early 20th century maximum, as deduced from the ice cores, occurred in two subsequent steps, whereas the emission inventory implies a more gradual increase throughout the 19th and early 20th century. Second, the BC inventory emissions remain fairly steady at high levels from AD 1910 to 1950 with no decrease between the two world wars as in both Alpine ice cores, and to some degree also in the Greenland ice cores (Fig. 5). Third, the emission inventories suggest that BC emissions dropped significantly since the 1960s and reached for OECD Europe pre-industrial levels by 1980, whereas BC ice-core concentrations remained clearly above their pre-industrial values until the very recent past. Median concentrations from 1980 onwards are still 3-fold at CG03 and 1.5-fold at FH02 compared to pre-industrial AD 1741–1850 levels, respectively. Table 3 summarizes BC emission estimates based on inventories and mean ice-core rBC concentrations centred at AD 1850, 1915, 1975, and 2000 for CG03, FH02 and a Greenland ice-core stack, respectively.
3.4 The timing of industrial BC deposition and glacier length variations in Europe in the 19th century
To test the plausibility of an ice-albedo effect to force (or at least contribute) to the glacier length reductions occurring during the 19th century we here examine the exact timing of industrial BC deposition at Colle Gnifetti and Fiescherhorn. For the latter, we interpret the sharp increase in EC (Fig. 3) in the sample dated to the years AD 1875 to 1879 (Jenk et al., 2006). Assuming conservatively that the increase occurred at the start age of this discrete sample and considering a dating uncertainty of ±5 years provides us with a lower bound for the earliest occurrence of enhanced BC deposition of AD 1870. ToE analysis for the CG03 rBCno BB record identifies the year AD 1875[5 %–95 % range: AD 1870–1882] as the time of emergence of industrial BC deposition with a conservative dating uncertainty of ±5 years (Fig. 7, Table 4). As ToE and dating uncertainty are independent, we estimate the absolute uncertainty range in the timing of industrial BC deposition at CG03 as AD 1868–1884 (5 %–95 % range). The Bayesian change-point algorithm returns virtually the same result, with the highest change point probability in AD 1876 (Table 4). The median timing of industrial BC deposition at the four Greenland ice-core sites is AD 1872 (ToE analysis) or AD 1891 (Bayesian change-point), respectively, in good agreement with the Alpine ice cores. Using the precisely dated D4 ice core and vanillic acid to discriminate forest fire emissions, McConnell et al. (2007) gave AD 1888 as their best estimate for industrial BC emergence, closely matching our best estimates, employing ToE analysis (AD 1878) and the Bayesian change-point method (AD 1891), respectively (Fig. S8)
The four high-resolution glacier length records indicate that in AD 1875 these glaciers had already completed the majority of their total cumulative length reductions (i.e. maximum to minimum front position) of the second half of the 19th century. Bossons had experienced 100 %, Oberer and Unterer Grindelwald 83 % and 74 %, respectively, and Mer de Glace 79 %, of their cumulative length losses (Table 4; Fig. 6e), with differences likely explained by the different size and topography of the individual glaciers (Lüthi, 2014). Consequently, the stacked record of all four glacier terminus position curves reveals that the highest annual mean glacier length reduction rates of >40 m year−1 occurred during the 1860s, when BC concentrations in both ice-cores were still indistinguishable from their natural background levels (Fig. 7). During time-of-emergence of industrial BC deposition in AD 1875 the stacked glacier record had experienced 83 % [52 %–92 %] of its entire cumulative glacier retreat from the maximum 1850s terminus positions. ToE analyses performed for total BC (ToE: AD 1890) and for calcium (ToE: AD 1986) are equally inconsistent with a mid-19th century emergence of the light-absorbing impurity content on Alpine glaciers outside the range of natural variability (Figs. S9, S10).
4.1 Alpine glacier fluctuations, industrial BC and post-volcanic cooling
For the first time, we are able to examine a continuous, well-dated record of BC from the pre-industrial into the most recent present at sub-annual resolution (Fig. 2). Highly reproducible rBC measurements mirror the low-resolution EC record obtained from the nearby Fiescherhorn ice core (Fig. 3). We interpret this as evidence that these ice cores detect a common signal of the atmospheric BC burden since the pre-industrial from anthropogenic emissions of BC by industrial and transport related activities. Other source tracers co-analysed with BC allow attribution of changes of the main emission sources to the observed trends (Fig. 4). During the pre-industrial (AD 1741–1850) CG03 rBC concentrations were low with episodic spikes co-registered with ammonium attributed to anthropogenic or natural biomass burning sources. Only later in the 19th century did concentrations of rBC and other industrial pollutants (e.g. Bi, Pb, ) typically emitted by coal burning start to increase significantly, with AD 1875 identified as the best estimate and AD 1868 as a very conservative lower bound for the timing of the earliest emergence of these emissions from background variability. Greenland ice cores, which also capture emissions from Europe, are consistent with our finding that no major increase of BC and other typically co-emitted industrial tracers (e.g. Bi) occurred before AD 1870 (Fig. 5). Mineral dust deposition at CG03 does not show relevant long-term trends during the 19th century.
The new combined evidence strongly contradicts the previous key assumption of a synchroneity between glacier retreat in the European Alps and BC increase in the 19th century in apparent support of the hypothesis that industrial BC emissions have forced accelerated glacier melt through a snow-albedo feedback (Painter et al., 2013). 82 % [52 %] of the glacier length reductions had already occurred at the best [earliest] estimated time of emergence of industrial BC deposition (Fig. 7). The discrepancy in the temporal relation between our results and those of Painter et al. (2013) are in part explained by the low resolution in their deployed glacier length records in the 19th century (i.e. Rhône, Argentière), that tend to smooth the actual terminus position curves between AD 1850 and 1900 and also by the limited quality of the BC records available at that time (see Sects. 1 and 3.2). As shown in Fig. 8, retreat rates of the terminus positions from high-resolution glacier observations were much stronger between AD 1850 and 1875 than they were between AD 1875 and 1900. Moreover, when industrial BC emissions reached their overall maximum values in the 1910–20s, indicated by ice-core BC concentrations exceeding 5 times their pre-industrial values, Alpine glaciers showed no indications of further retreat, but were instead advancing again (Figs. 7, 8). As our rBC measurement technique is less sensitive to “brown carbon” and mixed component aerosols and larger compounds outside the detectable size range (up to mass-equivalent diameter of 800 nm) such as produced by burning low quality coal or inefficient coal combustion (Sun et al., 2017), this record alone cannot rule out a potential role for other light-absorbing aerosols. However, these compounds are measured by the method applied for the EC record from FH02 which shows very good agreement with the rBC record from Colle Gnifetti (Sect. 3.2). This suggests that factors other than changes in surface snow albedo, such as temperature and seasonal precipitation distribution (Steiner et al., 2008; Zumbühl et al., 2008), may have dominated mass balance and glacier length variability of these European glaciers until at least AD 1875. The previously made claim (Painter et al., 2013; Vincent et al., 2005) that precipitation and temperature variability alone were insufficient to explain the observed glacier length variability has been recently challenged by Lüthi (2014) and Solomina et al. (2016), who demonstrated that on a regional to global scale summer temperatures are the most important parameters determining glacier mass balance variability. Previously underestimated due to an “early instrumental warm bias” (Böhm et al., 2010; Frank et al., 2007), new surface air temperature (SAT) reconstructions based on early instrumental records, historical documentary proxy evidence, and tree-rings now all give evidence that the early 19th century was exceptionally cold in Central Europe in a long-term context (Brohan et al., 2012; Büntgen et al., 2011; Luterbacher et al., 2016) (Figs. 9, S11). A strong negative radiative forcing resulting from at least five large tropical eruptions between 1809 and 1835 (Sigl et al., 2015; Toohey and Sigl, 2017), in tandem with the Dalton solar minimum (Jungclaus et al., 2017; Usoskin, 2013) appeared to have forced the glaciers to strongly advance until the 1850s, in some cases probably far outside their range of typical long-term natural variability (Fig. 8). Similarly, later glacier advances (e.g. in the 1890s and 1910s) followed other major volcanic eruptions including Krakatau (1883) and Katmai (1912) (Table 5).
A strong role of volcanic forcing is supported by a consistent strong coherence of glacier expansions following clusters of volcanic eruptions throughout the past 2000 years (Le Roy et al., 2015; Solomina et al., 2016). The stratospheric aerosol burden for the time window AD 1600–1840 was 40 % larger than during the entire Common Era (Sigl and Toohey, 2017) with volcanic eruptions frequently forcing cold spells and glacier advances (e.g. in 1600s, 1640s, 1820s, 1840s) in the Alps (Fig. 9) and elsewhere (Solomina et al., 2016). Increased summer precipitation during cool post-volcanic summers may have additionally contributed to a more positive mass balance (Raible et al., 2016; Wegmann et al., 2014) plausibly enforced by a positive albedo feedback loop resulting from increased snow cover in the Alps. The glaciers' initial and more or less synchronous retreat from the maximum terminus positions starting at 1860 may be a delayed rebound back to their positions they had before the radiative perturbed time period AD 1600–1840 (Fig. 9), and an additional decrease of snow albedo from the deposition of BC is considered not to be needed to explain these observations (Lüthi, 2014). The specific extent to which early anthropogenic warming (Abram et al., 2016), changes in atmospheric modes (Swingedouw et al., 2017) including the Atlantic Multidecadal Oscillation (AMO; Huss et al., 2010), or snow-albedo feedbacks from increasing light-absorbing aerosol deposition towards the end of the 19th century may have contributed to the overall glacier length variability in the European Alps throughout the 19th century remains difficult to determine. Confidently attributing and quantifying the contribution of natural and anthropogenic forcing to observed glacier changes will require reconciliation of early instrumental and proxy climate data (Böhm et al., 2010; Frank et al., 2007), and the use of models to decompose the relative contribution of volcanic eruptions, light-absorbing impurities such as BC or other compounds (e.g. brown carbon, mineral dust), and other potential natural or anthropogenic contributions (Goosse et al., 2018; Zekollari et al., 2014).
4.2 Constraints on Central European BC emissions
While the CG03 rBC time series reproduces the general major emission trends well from gridded BC emission inventories (Fig. 6) and it provides additional structure that is currently not captured by the BC inventories. This includes a stepwise increase of BC rather than linearly rising emissions; a short reduction of emissions between the two world wars likely related to global economic depression (Gabrieli and Barbante, 2014; Schwikowski et al., 2004) and smaller reductions since the 1960s as opposed to the BC emission inventories. Similar to Europe, Greenland ice-core BC records also do not support the idea of a gradual increase in BC since AD 1850 but show a very rapid increase of emissions around AD 1890, suggesting that the emission inventories data before AD 1900 may be biased. This is plausible given the small number and incomplete nature of consumption and technology-related records contributing to these inventories during this time (Bond et al., 2007, 2004). As many datasets (e.g. refinery outputs) during the 19th century were only available for the USA and with extrapolation backward in time applied often when specific data was unavailable (Bond et al., 2007) it is not surprising that the BC emission trend in Europe (and other regions) more or less closely follows that for North America prior to AD 1900 (Bond et al., 2007; Y. H. Lee et al., 2013). The discrepancy between the inventory-estimated and the much lower ice-core indicated reduction of BC in CG03 since the 1960s is striking. This mismatch suggests that the measures taken to reduce the release of BC into the atmosphere may not have been as efficient as the energy-consumption data suggests. This may hint that the emission factors (e.g. BC emitted per fossil-fuel unit burned) are frequently reported as too low in these inventories, which in the light of the Volkswagen emissions scandal revealed in 2015, seems at least a plausible scenario. A comparable offset had been recently also noted between modelled emissions and CG03 nitrate and ammonium records between 1995 and 2015 (Engardt et al., 2017) suggesting that besides rBC also NOx and NH3 emissions may not be adequately accounted for in present-day emission inventories. Greenland ice cores capturing mostly emissions from North America (where diesel engines play a minor role compared to Europe) in contrast to the alpine ice cores show a very pronounced decrease of BC during the second half of the 20th century to almost pre-industrial values at present (Keegan et al., 2014; McConnell et al., 2007). While providing more realistic estimates of carbonaceous particle emissions from gasoline and diesel engines remains an area of ongoing research (Gentner et al., 2012, 2017; Platt et al., 2017) more records are certainly required from other suitable sites in Europe to elude the sources of this late 20th century mismatch. Further reducing uncertainties in ice-core BC records is of eminent importance in assessing the accuracy of emission inventories and of particular interest as all state-of-the-art coupled aerosol climate models use gridded BC emission inventories as input parameters for their simulations (Lamarque et al., 2010; Y. H. Lee et al., 2013; Shindell et al., 2013).
Industrial black carbon believed to be emitted in large quantities starting in the mid-19th century had been suggested as the key external forcing responsible for an accelerated melting of European glaciers through reductions in ice-albedo and subsequent ablation (Painter et al., 2013). We examined this interpretation by presenting new, highly resolved, well replicated ice-core measurements of refractory black carbon, mineral dust, and distinctive industrial pollution tracers from the Colle Gnifetti ice core in the Alps covering the past 270 years. The comprehensive suite of elemental and chemical species co-analysed enabled BC source attribution from industrial and biomass burning emissions. The precisely dated ice core allowed precise comparison of the timing of observed acceleration of glacier retreat in the mid-19th century with that of increased deposition of black carbon on the glaciers caused by the industrialization in Europe. Closely reproducing the main structure of the Fiescherhorn EC record (Jenk et al., 2006), our study suggests that at the time when European rBC emission rates started to significantly increase (only after 1870) the majority of Alpine glaciers had already experienced more than 80 % of their total 19th century length reduction. Therefore, we argue that industrial BC emissions and subsequent deposition on Alpine glaciers are unlikely to be responsible for the rapid initial deglaciation at the end of the Little Ice Age in the Alps. We hypothesize that glacier length changes throughout the past 2000 years have been forced pre-dominantly by summer temperatures reductions induced by sulfuric acid aerosol forcing from large volcanic eruptions. In this sense, the retreat from the volcanically forced maximum glacier terminus positions starting in the 1860s can be seen as a lagged response of the cryosphere after the volcanic induced cooling had reached its maximum following a sequence of major tropical eruptions in AD 1809, 1815, 1823, 1831 and 1835. Only after AD 1870, when BC emissions started to strongly increase, snow-albedo impurity effects may have potentially contributed to the glacier length reductions.
Much of the understanding of future climate change is based on model simulations, but models used to predict future climate must be evaluated against past climate for accuracy (Hansen et al., 2007; Lamarque et al., 2013). Aerosols in climate models are mostly evaluated with observations from the past few decades, time periods during which mitigation measures for air quality control were widely in place. Ice-core records, possibly the only data sets to provide long-term historical information on aerosols, are thus critical for model evaluation, especially during time periods of widespread air pollution in industrialized countries during the 19th century. Here we present the first continuous BC record from Central Europe covering the past 270 years that has the resolution, precision, and reproducibility to serve in the future as a benchmark for climate models through dedicated model-data intercomparison (Koch et al., 2011; Y. H. Lee et al., 2013). Aerosol deposition at any single site also depends on factors such as atmospheric transport efficiency and the spatial distribution and conservation of snowfall. Incorporating more BC records from multiple sites into a stacked composite is expected to enhance the signal from the atmospheric burden over the noise caused by spatial variations in atmospheric transport and snow accumulation. Therefore, this should be considered a main focus for future research together with developing comparable records from other suitable ice-core sites in the Alps.
The CG03 ice-core data are available in the PANGAEA repository, https://doi.org/10.1594/PANGAEA.894788 (Sigl et al., 2018).
The supplement related to this article is available online at: https://doi.org/10.5194/tc-12-3311-2018-supplement.
MiS conceived this study, performed BC and ion analyses, developed age-models, analysed data, and wrote the paper; NJA performed ToE analyses; JG analysed trace elements, DO helped processing ice cores and developed SP2 methodology, TMJ supervised the development of the SP2 method and led the 2015 CG ice-core drilling campaign, MaS coordinated the project, and MiS led the manuscript writing with input from all coauthors.
The authors declare that they have no conflict of interest.
This work was supported by the Swiss National Science Foundation through the
research program “Paleo fires from high-alpine ice cores”
(CRSII2_154450/1). It was fostered by participation in the Volcanic Impacts
on Climate and Society (VICS) working group of PAGES (Past Global Changes).
The authors thank Joe R. McConnell and Nathan Chellman for providing
Greenland ice-core data; Matt Toohey for providing SAOD reconstructions;
Samuel Nussbaumer for providing glacier length reconstructions; Fang Cao for
providing the FH02 EC record; Carlo Barbante for partly funding the CG03
drilling campaign; Sabina Brütsch for ion chromatography analyses; and all
members of the CG ice-core drilling expeditions in 2003, 2008 and 2015. We
also would like to thank Thomas Painter and colleagues and the three
anonymous reviewers for their comments and valuable input helping to improve
Edited by: Becky Alexander
Reviewed by: three anonymous referees
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