Crop stalks (CSs) are common agricultural wastes in China. The annual yield of CSs in China is ca. 0.7 billion tons, 1 but only 1 / 3 of CSs is used. The problem of dealing with tons of CSs needs to be solved urgently. Part of CSs is piled up along roads, ditches, and even beside houses, which occupies a lot of space and hinders the traffic. During harvest seasons, most of the CSs in China are burned to ensure normal farming. 2 CS combustion in the field degrades air quality by emitting soot, carbon monoxide, methane, and other volatile organic compounds and forming aerosol. 2−9 Condensed aromatics (CAs) are important parts of aerosol and ubiquitous in the environment. 10−12 They are primarily generated from anthropogenic pollution, such as incomplete combustion of oil and biomass in boiler, heating installation, commercial installation, and engine. 8,13 CAs associate with inhalable particles, resulting in harm to human health as a result of the teratogenicity, carcinogenicity, and mutagenicity. 13−16 They tend to accumulate in aquatic organisms and plants or form more virulent products under effects of photoinduction, bioaccumulation, or biological processes in rivers, lakes, oceans, and soil. Quite a few studies, including volatilization, photo-and chemical oxidation, adsorption to soil particles, leaching, and biodegradation, were focused on seeking solutions to the pollution from CAs. 10,13 However, the methods are considered as treatments after CAs enter the environment. It is urgent and necessary to find a clean way to use CSs and avoid CAs emitting to the environment. In the present investigation, we tried to understand the modes of CA occurrences in wheat stalk (WS) by degradation of the WS in supercritical ethanol, column chromatography of degraded WS, and subsequent analysis of the eluted fractions with gas chromatography/mass spectrometry (GC/MS).The WS was collected from a Xuzhou suburb, Jiangsu province, China. It was pulverized to pass through an 80-mesh sieve and dried in a vacuum oven at 105 °C for 3.5 h. Table 1 shows proximate, ultimate, and chemical analyses of the sample. All of the solvents used in the experiment, including petroleum ether (PE), methyl acetate (MA), and ethanol, are analytical reagents and distilled prior to use. Silica gel (SG, 100−200 mesh) was activated in a vacuum oven at 145 °C for 6 h before use. As Figure 1 shows, 10 g of WS and 300 mL of ethanol were put into a 500 mL stainless-steel, magnetically stirred autoclave. The autoclave was heated to 300 °C within 1 h, kept at that temperature for 0.5 h, and then immediately cooled to room temperature in an ice−water bath. The reaction mixture was