Permafrost

Identification

1.	Description

This indicator shows trends in Alaskan permafrost temperature based on borehole measurements.
Permafrost is defined as rock or soil and included ice that remains at or below 0°C (32°F) for two or
more years and usually occurs beneath the active layer, which annually freezes and thaws (IPCC, 2019).
The continuity and classification of permafrost coverage changes latitudinally and is dependent on land
cover type, slope, and other local environmental characteristics. Permafrost is particularly sensitive to
changing climatic conditions, notably rising surface air temperatures and changing snow regimes (IPCC,
2019; Smith et al., 2010). At depths of 10 to 200 meters (32.8 to 656.2 feet), the permafrost
temperature regime is a highly sensitive indicator of long-term climatic variability. This is because
interannual temperature ranges decrease significantly with increases in depth, allowing for the
observation of precise, decadal temperature variation (Yershov, 1998). Changing permafrost
temperature can amplify global climate change, as thawed sediments unlock and release soil organic
carbon—including methane, which has a high global warming potential—into the carbon cycle (Schaefer
et al., 2014). Other consequences of permafrost thaw include but are not limited to building foundation
failure and decreased infrastructure stability, as well as decreases in slope stability that can lead to
destabilized mountain structure and slope failure. As a subsurface phenomenon, the temporal changes
and spatial distribution of permafrost cannot easily be observed, unlike glaciers and polar sea ice (IPCC,
2019). However, the connection between permafrost temperature and climate change can be
determined through a reproducible data collection regime at specific borehole sites throughout Alaska.

Components of this indicator include:

•	Time series of soil temperatures in interior and northern Alaska boreholes, from 1978 to present
(Figure 1).

•	A map of borehole sites with accompanying temperature trend visualization (Figure 2).

2.	Revision History

April 2021: Indicator published.

Data Sources

3. Data Sources

Both figures use yearly observational data provided by Dr. Vladimir E. Romanovsky and the Permafrost
Laboratory in the Geophysical Institute of the University of Alaska Fairbanks. Data are collected annually
via boreholes across Alaska. The best way to characterize temporal trends in permafrost temperature is
to collect consistent, long-term observations at designated borehole stations (Romanovsky et al., 2010).
Borehole data continue to be measured by the University of Alaska Fairbanks.

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4. Data Availability

Borehole temperature data are publicly available from the Permafrost Laboratory of the University of
Alaska Fairbanks, along with corresponding metadata, at: https://permafrost.gi.alaska.edu/sites map.
Users can learn more about the methodology at: https://permafrost.gi.alaska.edu/content/methods.
More information about the work of the Permafrost Laboratory is detailed on their website:
https://permafrost.gi.alaska.edu/about.

Some of the data used in this indicator are also publicly available online at the NSF Arctic Data Center at:
https://arcticdata.io/catalog/data. Additionally, borehole data on a global scale are publicly available
from the Global Terrestrial Network for Permafrost (GTN-P) at: https://gtnp.arcticportal.org. The GTN-P
is an international program tasked with monitoring permafrost. It was developed by the International
Permafrost Association under the Global Climate Observing System and the Global Terrestrial Observing
Network in 1999. Its long-term goal is to obtain a complete view of the trends, spatial composition, and
variability of changes in permafrost structure and temperature (Biskaborn et al., 2015, 2019).

EPA worked directly with Dr. Vladimir E. Romanovsky to obtain a compilation of data for all the specific
sites and years covered by this indicator.

Methodology	

5. Data Collection

This indicator is based on observational research and measurements by the University of Alaska
Fairbanks. Data measurements are divided between two primary study regions: Interior Alaska and
Northern Alaska. Data collection periods of record vary by region and by site.

Within the Northern Hemisphere polar region, ground temperatures are being measured in
approximately 575 boreholes throughout North America, the Nordic regions, and Russia (Romanovsky et
al., 2010)—including more than 100 in Alaska. For many sites, though, the record length is too short, the
methods used vary, or data are not complete enough for comparability or long-term trend assessment.
Therefore, this indicator focuses on a subset of 15 sites with the longest and most complete data record
to characterize trends related to climate. Table TD-1 identifies these sites, their corresponding study
regions, and the depth of measurements used in this indicator. The sites selected for this indicator are
also consistent with other published permafrost indicators (e.g., Blunden and Arndt, 2019; Romanovsky
et al., 2017).

In the interior Alaska study region, the earliest measurement across the eight selected borehole sites is
from 1983. In the northern Alaska study region, the earliest measurement across the seven selected
borehole sites is from 1978. Both study regions contain data until 2020, with updated data collected on
an annual basis. The average number of yearly data points per borehole in interior Alaska is 29.5
(standard deviation = 3.91), and the average number of yearly data points per borehole in northern
Alaska is 30.29 (standard deviation = 10.79). At a few sites, data could not be collected in 2020 because
of the COVID pandemic.

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Borehole sites used in this indicator are established in undisturbed areas and span a wide range of
permafrost, climatic, and environmental conditions. The majority of sites are located along or near the
International Geosphere-Biosphere Programme Alaskan transect, which runs across the entire state of
Alaska from north to south (see Figure 2). Site elevations range from 2.7 to 976.3 meters (9 feet to 3,203
feet) above sea level, with an average of 312.2 meters (standard deviation = 298.3) (1024.3 feet,
standard deviation = 978.6).

The manual at: https://permafrost.gi.alaska.edu/sites/default/files/TSP manual.pdf provides details
about measurement. Some boreholes use continuous observations with automated sensors that report
with hourly or daily frequency; the standard is every six to eight hours. Others use less frequent, non-
automated measurements. Temperature readings at all sites are measured by either a Measurement
Research Corporation 107 Temperature Probe or an Onset Computer Corporation StowAway (XTI or
Optic) sensor. Sensors are calibrated in the field to ensure accuracy.

Temperature at each site is measured at multiple depths, typically at intervals of 2 meters (6.6 feet).
Most of the sites in this study have their shallowest measurement at 6 meters (19.7 feet) below ground
level. Differences in the suitability of local conditions between sites necessitates variation of the
shallowest measurement depth. The deepest measurements range from 28 to 75 meters (91.9 to 246.1
feet) below ground. Table TD-1 lists the depth selected for long-term trend analysis at each site, based
on the approach described in Section 6 below.

Table TD-1. Borehole Locations and Measurement Depths Used for This Indicator

Region

Borehole location

Measurement depth



Old Man

15 meters (49 feet)



Birch Lake

15 meters (49 feet)



Chandalar Shelf

20 meters (66 feet)

Interior Alaska

Coldfoot

26 meters (85 feet)



College Peat

20 meters (66 feet)



Livengood

15 meters (49 feet)



Healy

15 meters (49 feet)



Gulkana

15 meters (49 feet)



Galbraith Lake

20 meters (66 feet)



Happy Valley

20 meters (66 feet)



Franklin Bluffs

20 meters (66 feet)

Northern Alaska

Kaktovik (ANWR/Barter)

20 meters (66 feet)



Deadhorse

20 meters (66 feet)



Barrow 2 (N. Meadow Lake No. 2/NML-2)

16 meters (53 feet)



West Dock

20 meters (66 feet)

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6. Derivation

This indicator is based on measurements that are most representative of annual average conditions in
each borehole. Where multiple timestamps are available (in the case of sites with automated
temperature sensors), annual averages are used. At each site, one representative depth was chosen for
use in this indicator. The most appropriate depth for use is the depth of zero annual amplitude—i.e., the
shallowest depth where seasonal variations of ground temperature become negligible. This condition
occurs at different depths in different locations, ranging from a few meters in warm, ice-rich permafrost
to 20 meters or more in cold permafrost and bedrock (AMAP, 2017). For most of the sites used for this
indicator, the selected depth was either 15 or 20 meters (49.2 or 65.6 feet). Measurements from 26
meters (85.3 feet) were used at one site where that was the shallowest measurement available in all
years.

The graph in Figure 1 shows the temperature measurements recorded each year at the specified depths.
No further calculations or transformations were needed to generate these time series.

The map in Figure 2 shows a long-term rate of temperature change at each site. EPA calculated this rate
of change by performing an ordinary least-squares linear regression with the data for each site, then
multiplying the regression slope by 10 to derive an average rate of temperature change per decade. The
map shows results at each site, with no attempt to generalize or model results over space.

7. Quality Assurance and Quality Control

The University of Alaska Fairbanks conducts quality assurance and quality control (QA/QC) activities
prior to data distribution. Key steps include equipment calibration before collecting measurements.

Additionally, sites in disturbed areas or sites that became disturbed (i.e. wildfire, infrastructure changes,
etc.) are removed from the analysis to ensure data quality. The indicator does not include sites with data
collection methods that differed from the University of Alaska Fairbanks' standardized data collection
protocol.

Additional QA/QC procedures for manual measurements are largely unavailable online. Data used in this
indicator have been peer-reviewed and published by reputable scientific journals, reports, and other
texts.

Analysis	

8. Comparability Over Time and Space

For consistency, this indicator examines trends at depths that are selected to be most representative of
average conditions throughout the year. Borehole sites do not change location, providing spatial
consistency.

Data collection methods may have changed slightly with advancements in probe technology. The
University of Alaska Fairbanks, however, has taken careful steps to calibrate and quality-check their
equipment before data collection and dissemination (see Section 7). Standardized data collection and
QA/QC protocols ensure methods are applied consistently over time and space.

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9. Data Limitations

Factors that may impact the confidence, application, or conclusions drawn from this indicator are as
follows:

1.	Some borehole sites rely on data collected at depths less than 20 meters (66 feet), which may
be subject to notable influence by seasonal or short-term surface temperature changes.
Permafrost temperature measurements 20 meters and deeper are not affected by seasonal
variation and are therefore considered ideal for identifying long-term trends (Romanovsky et al.,
2007).

2.	Gaps in the dataset produce an imperfect estimation of potential permafrost temperature
trends. The gap around 2003-2004 reflects a period in which the monitoring program and
dataset were transition from one research team to another. However, all sites included in this
indicator have sufficient data for trend analysis. Sites with larger data gaps (> five years
consecutive and seven years overall) have been excluded from the analysis.

3.	Due to local environmental characteristics, this collection of sites is not necessarily indicative of
all varieties of permafrost and the associated temperature trends. Permafrost is highly variable,
and permafrost temperature is linked with multiple environmental factors such as soil type,
aspect, and snow cover depth (Smith et al., 2010). Most notably, permafrost in interior Alaska is
naturally warmer and less continuous than permafrost in northern Alaska. For these reasons,
among others, this indicator focuses more on individual site temperature comparisons over time
and less on inter-site comparisons. This variation must be kept in mind when looking at
permafrost temperatures at larger regional or pan-Arctic scales.

10.	Sources of Uncertainty

A small amount of uncertainty is inherent due to the temperature measurement system at each
borehole. However, the measurement methodology used throughout the period of record generally
provides an accuracy and precision of 0.1°C (0.18°F) or better (Romanovsky et al., 2010).

Differences in environmental characteristics at specific borehole sites may introduce uncertainty to the
indicator, although the broad spatial distribution provides a degree of certainty to the analysis. A diverse
collection of sites nearly all trending in the same direction suggests the presence of a broader-scale
influence and change that is more than just the result of specific local factors.

Calculating temperature trends when data gaps are present adds a small amount of uncertainty to the
indicator.

11.	Sources of Variability

Natural year-to-year variations in snowfall, surface temperature, air temperature, and other climate
variables may directly influence short-term permafrost temperatures. This indicator looks at longer-term
temporal trends with a wide degree of spatial variation, thus reducing the influence of year-to-year
variability. Over a longer timeframe, non-climatic factors such as land-use change, anthropogenic
disturbance, and wildfire can influence permafrost temperature trends. Borehole sites were chosen to
specifically avoid these non-climatic factors, although minor influences are possible.

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12. Statistical/Trend Analysis

Figure 2 displays long-term trends based on a least-squares linear regression of annual observations at
each borehole site for the site's period of record. The statistical significance of each of these trends was
examined based on the p-values of these regressions. Of the 15 sites, all but Livengood and College Peat
had a trend that was significant to a 95 percent level (p < 0.05).

References

AMAP (Arctic Monitoring and Assessment Programme). 2017. Snow, water, ice and permafrost in the
Arctic (SWIPA) 2017. https://www.amap.no/documents/doc/snow-water-ice-and-permafrost-in-the-
arctic-swipa-2017/1610.

Biskaborn, B.K., J-P. Lanckman, H. Lantuit, K. Elger, D.A. Streletskiy, W.L. Cable, and V.E. Romanovsky.
2015. The new database of the Global Terrestrial Network for Permafrost (GTN-P). Earth Syst. Sci. Data
7:245-259.

Biskaborn, B.K., et al. 2019. Permafrost is warming at a global scale. Nat. Commun. 10:264.
doi: 10.1038/s41467-018-08240-4

Blunden, J., and D.S. Arndt (eds.). 2019. State of the climate in 2018. Bull. Amer. Meteor. Soc. 100(9):S1-
S305. doi:10.1175/2019BAMSStateoftheClimate.l

IPCC (Intergovernmental Panel on Climate Change). 2019. Summary for policymakers. In: IPCC special
report on the ocean and cryosphere in a changing climate. Portner, H.-O., D.C. Roberts, V. Masson-
Delmotte, P. Zhai, M. Tignor, E. Poloczanska, K. Mintenbeck, M. Nicolai, A. Okem, J. Petzold, B. Rama,
and N. Weyer (eds.). https://report.ipcc.ch/srocc/pdf/SROCC Final Draft FullReport.pdf.

Romanovsky, V.E., S. Gruber, A. Instanes, H. Jin, S. Marchenko, S.L. Smith, D. Trombotto, and K.M.
Walter. 2007. Chapter 7: Frozen ground. In: Global outlook for ice and snow. Birkeland, Norway: United
Nations Environment Programme, pp. 181-200.

Romanovsky, V.E., S.L. Smith, and H.H. Christiansen. 2010. Permafrost thermal state in the polar
Northern Hemisphere during the international polar year 2007-2009: A synthesis. Permafrost Periglac.
Process. 21:106-116. doi:10.1002/ppp.689.

Romanovsky, V., et al. 2017. Changing permafrost and its impacts. In: AMAP (Arctic Monitoring and
Assessment Programme). Snow, water, ice and permafrost in the Arctic (SWIPA) 2017. pp. 65-102.
https://www.amap.no/documents/doc/snow-water-ice-and-permafrost-in-the-arctic-swipa-2017/1610.

Schaefer, K., H. Lantuit, V.E. Romanovsky, E.A. Schuur, and R. Witt. 2014. The impact of the permafrost
carbon feedback on global climate. Environ. Res. Lett. 9:085003.

Smith, S.L., V.E. Romanovsky, A.G. Lewkowicz, C.R. Burn, M. Al lard, G.D. Clow, K. Yoshikawa, and J.
Throop. 2010. Thermal state of permafrost in North America: A contribution to the international polar
year. Permafrost Periglac. Process. 21:117-135.

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Yershov, E.D. 1998. General geocryology. Cambridge, UK: Cambridge University Press.

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