The Cryosphere, 4, 475–487, 2010 www.the-cryosphere.net/4/475/2010/ The Cryosphere doi:10.5194/tc-4-475-2010 © Author(s) 2010. CC Attribution 3.0 License. Monitoring of active layer dynamics at a permafrost site on Svalbard using multi-channel ground-penetrating radar S. Westermann1, U. Wollschlager¨ 2,*, and J. Boike1 1Alfred-Wegener-Institute for Polar and Marine Research, Telegrafenberg A43, 14473 Potsdam, Germany 2Institute of Environmental Physics, Ruprecht-Karls-University Heidelberg, 69120 Heidelberg, Germany *now at: UFZ – Helmholtz Centre for Environmental Research, Permoserstraße 15, 04318 Leipzig, Germany Received: 11 March 2010 – Published in The Cryosphere Discuss.: 22 March 2010 Revised: 28 October 2010 – Accepted: 29 October 2010 – Published: 8 November 2010 Abstract. Multi-channel ground-penetrating radar is used to mafrost areas. The novel non-invasive technique is partic- investigate the late-summer evolution of the thaw depth and ularly useful when the thaw depth exceeds 1.5 m, so that it the average soil water content of the thawed active layer at a is hardly accessible by manual probing. In addition, multi- high-arctic continuous permafrost site on Svalbard, Norway. channel ground-penetrating radar holds potential for map- Between mid of August and mid of September 2008, five ping the latent heat content of the active layer and for esti- surveys have been conducted in gravelly soil over transect mating weekly to monthly averages of the ground heat flux lengths of 130 and 175 m each. The maximum thaw depths during the thaw period. range from 1.6 m to 2.0 m, so that they are among the deepest thaw depths recorded in sediments on Svalbard so far. The thaw depths increase by approximately 0.2 m between mid 1 Introduction of August and beginning of September and subsequently re- main constant until mid of September. The thaw rates are About 24% of the land area of the Northern Hemisphere is approximately constant over the entire length of the tran- underlain by permafrost, of which most occurs in arctic re- sects within the measurement accuracy of about 5 to 10 cm. gions (Brown et al., 1997). These regions are anticipated to The average volumetric soil water content of the thawed soil be severely affected by climate change (e.g. Overland et al., varies between 0.18 and 0.27 along the investigated transects. 2008), and a considerable reduction of the permafrost area While the measurements do not show significant changes is projected until 2100 (e.g. Delisle, 2007; Lawrence et al., in soil water content over the first four weeks of the study, 2008). The warming will have strong impacts on the ecology strong precipitation causes an increase in average soil water (e.g. Jorgenson et al., 2001), infrastructure (Parker, 2001) content of up to 0.04 during the last week. These values are and economy (Prowse et al., 2009) of the arctic permafrost in good agreement with evapotranspiration and precipitation regions. A sustained warming trend in the Arctic over the rates measured in the vicinity of the the study site. While past decades has been revealed by a number of studies (e.g. we cannot provide conclusive reasons for the detected spatial Serreze et al., 2000; Comiso and Parkinson, 2004), which is variability of the thaw depth at the study site, our measure- also reflected in widely increasing permafrost temperatures ments show that thaw depth and average soil water content (e.g. Hinzman et al., 2005; Osterkamp, 2005). are not directly correlated. The degradation of permafrost usually is preceded by an The study demonstrates the potential of multi-channel increase in the thickness of the active layer, followed by the ground-penetrating radar for mapping thaw depth in per- formation of a talik and the subsequent thawing of the re- maining permafrost body from top and bottom. An ongo- ing monitoring of the active layer thickness might therefore Correspondence to: S. Westermann serve as an “early-warning system” to detect the onset of ([email protected]) permafrost degradation. Recent studies suggest an increase Published by Copernicus Publications on behalf of the European Geosciences Union. 476 S. Westermann et al.: Monitoring of active layer dynamics using multi-channel GPR of the thaw depth in permafrost areas (Oelke et al., 2004; et al., 2001; Moorman et al., 2003; Schwamborn et al., 2008). Zhang et al., 2005), while others do not detect an increase Bradford et al. (2005) and Brosten et al. (2006) use GPR in thaw depth despite of a warming of the permafrost tem- to monitor the seasonal dynamics of the thaw bulb beneath peratures (Osterkamp, 2007). On Svalbard, considerable in- small streams in permafrost regions. In the framework of the terannual variations of the active layer thickness are com- CALM program, the use of GPR for mapping thaw depth mon (Christiansen and Humlum, 2008; Christiansen et al., has been proposed by Brown et al. (2000), but the tech- 2010) which might obscure long-term trends. In the Kap nique has not become established yet. GPR is well suited Linne´ area, Akerman˚ (2005) reports an increase of the active for investigating thaw depth, as the abrupt increase of the layer thickness since the 1980s in conjunction with increas- dielectric permittivity at the interface between thawed and ing air temperatures. Isaksen et al. (2007) report increasing frozen soil induces a strong reflection of the electromagnetic permafrost temperatures in a borehole in Nordenskioldland¨ signal. However, lateral variations of the soil water con- during the last decade, which is accompanied by a moderate tent cause a non-constant velocity of the GPR signal (e.g. increase in active layer thickness by 10 to 30 cm. Davis and Annan, 1989), which can lead to a considerable The active layer, defined as “the top layer of ground sub- bias in the reflector depth, if the signal velocity is only cal- ject to annual thawing and freezing in areas underlain by per- ibrated at a few points (Moorman et al., 2003; Wollschlager¨ mafrost” (Harris et al., 1988), is the biologically active zone et al., 2010). These difficulties can be overcome by the use of the soil, where formation and decomposition of organic of multi-channel systems, which are capable of simultane- material can occur. Zimov et al. (2006) suggest that degra- ously mapping the reflector depth and the average soil wa- dation of permafrost and an increase in active layer thickness ter content between surface and reflector (Bradford, 2008; will make large amounts of previously frozen organic mate- Gerhards et al., 2008). For a permafrost site on the Qinghai- rial available for decomposition, which may lead to a mas- Tibet Plateau, Wollschlager¨ et al. (2010) demonstrate that the sive release of methane and carbon dioxide from permafrost permafrost table and the average soil water content above regions. The activation of this carbon stock would convert the frost table can be surveyed with horizontal resolutions northern permafrost regions from net sinks to net sources of of less than one meter, which would be extremely arduous greenhouse gases (Schuur et al., 2008), resulting in an am- to achieve by a manual method. However, to successfully plification of the global warming trend. To develop realis- monitor the seasonal dynamics of the thaw depth, it must tic predictions for this scenario, it is imperative to map and be guaranteed that consecutive measurements with multi- monitor the dynamics of the active layer and understand the channel GPR yield consistent results. controlling factors for the seasonal thawing. In this study, we present a time series of multi-channel In the framework of the “Global Terrestrial Network- GPR measurements of the thaw depth and soil water content Permafrost” (GTN-P), the “Circumpolar Active Layer Moni- at a high-arctic site on Svalbard, Norway, over the course of toring” program (CALM) has provided measurements of the five weeks. At the chosen study site, rocky soil and thaw active layer thickness at more than 150 sites (Nelson et al., depths exceeding 1.5 m effectively prevent the use of manual 2008). At some sites, repeated measurements are performed probing methods. The study is conducted at the end of the to resolve the seasonal evolution of the thaw depth (e.g. Shik- thaw season from mid of August until mid of September, so lomanov et al., 2008). These measurements are traditionally that the late-summer maximum thaw depth of the active layer conducted manually using a frost probe (Brown et al., 2000). can be inferred from the measurements. On an area of 100×100 m2 or larger, many single probings are performed to account for a potential spatial variability of the thaw depth and to limit the impact of single erroneous 2 Study site probings due to stones or other impenetrable structures in the ground. The method is satisfactory in soft soils, where The study site is located between the glacier Brøggerbreen the thaw depth does not greatly exceed one meter. In rocky and the Kongsfjorden at 78◦550 N, 11◦500 E, approximately soils or in case of much greater thaw depths, manual methods 2 km SW of the village of Ny-Alesund.˚ Due to the influ- become increasingly difficult: the frost probe cannot pene- ence of the North Atlantic Current, the area features a mar- trate easily to the frost table, so that it becomes hard to verify itime climate with cool summers and relatively mild win- that it has been reached (Hinkel and Nelson, 2003). As a ters. The coldest month is February with an average air future increase in active layer thickness is likely for many temperature of around −14 ◦C, while the average air tem- of the existing CALM sites, it is desirable to develop and perature is around +5 ◦C during the warmest month July validate alternative methods for the monitoring of the active (www.eklima.no, 2010).