**Background:** Wetland ecosystems in high-latitude regions are major reservoirs for pollutants. Climate warming is causing permafrost degradation in cryolitic peatlands, risking the release of heavy metals (HMs) into the Arctic Ocean basin. The subarctic European Northeast is particularly climate-sensitive, with the seasonally thawed layer (STL) being the most temperature-vulnerable permafrost soil segment. This study aimed to (1) quantify HMs and As across Histosol profiles in background and technogenic Subarctic landscapes, (2) evaluate anthropogenic contributions from energy plants to trace element accumulation in the STL, and (3) identify the effects of biogeochemical barriers on vertical HM and As distribution.
**Methods:** Peat samples were collected every 5–10 cm from three plots: two background sites (Plot 1 and Plot 2, 20 km SE of Inta) and one technogenic site (Plot 3, 5 km NW of Inta, near the Inta coal heat power plant). Sampling depths reached 2.6 m (Plot 1), 1.8 m (Plot 2), and 2.5 m (Plot 3). Acid-soluble forms of macroelements (Na, K, Mg, Ca, Al, Fe) and HMs (Hg, Pb, Cd, Cu, Zn, Cr, V, Ni, Mn, Co, Sr, Ba), S, P, and As were analyzed by inductively coupled plasma atomic emission spectroscopy (Spectro Arcos, Spectro Cyros CCD). Total Hg was determined by atomic absorption spectroscopy (RA-915+). Water-soluble forms and exchangeable Ca/Mg were also measured. Mineral particle morphology was examined by scanning electron microscopy (Tescan Vega 3 LMH) with energy-dispersive X-ray spectroscopy (X-MAX 50). Humic (HAs) and fulvic acids (FAs) were extracted per IHSS method. Radiocarbon dating (^14^C) was performed at the Institute of Geography RAS (lab code IGAN). Statistical analyses included Pearson correlation and principal component analysis (PCA) using Statistica v. 12.1.
**Key Results:** Radiocarbon dating showed peat accumulation began in the late boreal period (8953 cal year BP), with the most intense accumulation during the Atlantic period (8953–5661 cal years BP). The STL peat was acidic (pH 3.4–4.0). Ash content in background STL peat was 2–6% (carbon 54–59%), while Plot 3 reached 11% ash. The upper level of microelement accumulation was associated with the STL. The total concentration factor (ΣKi) relative to Earth's crust decreased down-profile to the permafrost boundary (40 cm) from 8.7 to 4.4 for Plot 3 and from 6.8 to 2.5 for Plot 1. Below permafrost, ΣKi increased to 2.3–18.0, with As exceeding clarkes up to 4.0 times and Cd up to 2.3 times. Plot 3 showed excess over background of Hg (1.2×), Cd (1.6×), Pb (2.0×), Cu (3.1×), As (1.2×), Ni (1.8×), Co (2.1×), Cr (3.7×), V (3.3×), and Fe (4.6×). Spheroidal microparticles (<1 μm to 30–50 μm) composed of aluminosilicates with iron oxides and trace metals were found only in the upper 5 cm of Plot 3, serving as indicators of coal combustion pollution. At the permafrost boundary, the proportion of water-soluble forms increased for Pb (up to 1.4%), V (up to 2.1%), Cr (up to 2.7%), Cd (up to 3.4%), Zn (up to 4.0%), Mn (up to 7.1%), and As (up to 15%). Significant correlations were found between Hg and HAs (r = 0.65, n = 29), and between Cd, Zn, Mn, K, Na, Mg and FAs (r = 0.52–0.71). In the PL, significant correlations were found between total sulfur and chalcophile elements (Hg r = 0.57, Cd r = 0.61, Cu r = 0.66, As r = 0.53), and between Fe/Al and siderophile elements (Ni, Cr, Mn, Co, V; r = 0.76–0.96, n = 43, p = 0.95). PCA for STL samples explained 75.36% of variability (PC1 50.67%, PC2 24.70%); for PL samples, 71.04% (PC1 56.75%, PC2 14.29%).
**Clinical Implications:** This study provides critical baseline data on HM and As concentrations in Subarctic peatlands, demonstrating that permafrost acts as a geochemical barrier trapping toxicants. With climate warming, permafrost thaw could mobilize these pollutants into hydrological networks and food chains, posing environmental and public health risks to Arctic communities. The identification of spheroidal microparticles as markers of coal combustion pollution offers a monitoring tool for industrial impacts. The findings underscore the need for environmental monitoring of HMs in permafrost regions undergoing climate-driven degradation.