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Chapter 8:Hazard Analysis—Lava and VOG <br /> the recently formed pit) there can also be contributions (of water vapor, hydrogen sulfide, <br /> and sulfur trioxide) from lower temperature hydrothermal systems that surround the magma <br /> conduit below and around Halema'uma'u. <br /> Soon after the gases discharge from the magma or the conduit surfaces, they begin to cool <br /> and undergo a variety of internal reactions and reactions with the atmosphere. While in the <br /> gas phase all the above compounds are transparent but, with cooling, sulfur trioxide will <br /> rapidly combine with water vapor(from the plume or the atmosphere) to form a sulfuric acid <br /> (H2SO4) aerosol. Under relatively dry conditions, the sulfuric acid aerosol can be <br /> distinguished by its bluish cast; when abundant water is present, a dense white plume is <br /> formed. HCl and HF will also condense onto solid particulates, if the latter are present, or <br /> form aerosol droplets by combining with condensing water vapor. Under dry atmospheric <br /> conditions, the plume will drift downwind and mix with the air column which will decrease <br /> the dew point in the discharge plume and the aerosol droplets will dehydrate and disperse. <br /> Under moist conditions, the plume will remain hydrated and the aerosols will remain much <br /> more visible. <br /> Mixing with air will also lead to reactions between atmospheric oxygen and the sulfur <br /> compounds sulfur dioxide and hydrogen sulfide. Sulfur dioxide is the more reactive of the <br /> two, with reported half-lives as short as a few tens of minutes to as long as several days <br /> depending on the chemical constituents in the air mass (e.g. urban air pollution, marine air), <br /> as well as the intensity of ultraviolet radiation. Given the absence of significant sulfur <br /> dioxide in the vog plume by the time it reaches Kona, it's likely that the half-life in the <br /> Hawaii air mass is no more than a few hours. The oxidation of any hydrogen sulfide present <br /> in the plume occurs at a much slower rate where the half-life of HZS in the atmosphere may <br /> be a day or more. <br /> The oxidation of sulfur dioxide will result in the formation of additional sulfur <br /> trioxide/sulfuric acid aerosol (because sulfur trioxide is extremely hygrosocopic, it will <br /> extract nearly any and all available water vapor from the atmosphere to form the acid <br /> aerosol) to contribute to the dry haze in the downwind plume. The oxidation process will <br /> continue until all of the sulfur dioxide is converted to sulfuric acid. <br /> Mixing of the plume with the atmosphere also brings the plume constituents into contact with <br /> ammonia that is derived from biogenic decay processes occurring in tropical soils. In the <br /> presence of water, ammonia (NH3) forms a weak base (NH40H) that will react very rapidly <br /> with the sulfuric acid aerosols to form ammonium sulfate [(NH4) 2SO41, and with the <br /> hydrochloric and hydrofluoric acids to form ammonium chloride (NH4C1) and ammonium <br /> fluoride (NH4F) respectively. Although these ammonia salts are not as hygroscopic as sulfur <br /> trioxide, they are sensitive to atmospheric moisture levels and the optical density of the <br /> plume will vary depending on the relative humidity in the ambient air. <br /> Whereas the non-reactive gas phase components of the plume (e.g. carbon dioxide) will <br /> gradually disperse, the aerosols are subject to both gravitational settling, through a process <br /> called dry deposition, as well as scrubbing from the atmosphere by rainfall. Although the <br /> aerosols can serve as a source of condensation nuclei for raindrop formation, some studies <br /> 8-5 Hawaii County Multi-Hazard Mitigation Plan <br />