Petrographic and physico-chemical analyses of ashes are carried out on a large scale and presented in numerous scientific papers. The mentioned ashes are obtained from filters and electrostatic precipitators mounted in large industrial installations. The large-scale analysis of the ashes obtained directly from grate furnaces or blast furnaces mounted in low-power boilers started with combating smog and low-stack emissions. The collection of ash samples from household furnaces usually involves the analysis of the combustion of waste in low-power boilers. This is justified in the case of old type boilers, which were designed to use virtually any fuel. Currently, new types of boilers, designed to burn dedicated fuels, are offered on the market. The aim is to use only renewable fuels (biomass) or fossil fuels with high quality parameters, which are more environment-friendly, e.g. eco-pea coal, lignite briquettes, or peat briquettes. The authors of the study focused on examining the ash obtained from boilers for burning wood pellets by performing microscopic analysis of residues after biomass combustion. The above mentioned analysis provides a comprehensive information on the efficiency of the combustion process, the content of contaminants remaining in the ash, and the suitability of ash for other applications. The entire process, from the moment of collecting the samples to the execution of the analysis takes up to 12 hours, which ensures a quick decision on furnace adjustment or fuel change. The ash components were determined based on the results obtained by the Fly-Ash Working Group of the International Committee for Coal and Organic Petrology (ICCP). The mentioned classification has been supplemented with new key elements occurring in ashes resulting from the combustion of wood pellets in household boilers. This allowed determining the percentage content of characteristic components in the tested material, which can be used as a specific benchmark when issuing opinions on the quality and efficiency of the boiler and the combusted pellets.

Spalanie odpadów komunalnych w domowych piecach to problem, z którym boryka się wiele polskich samorządów. Zarządzanie procesami zwalczania i zapobiegania tym zjawiskom jest niezwykle trudne, ponieważ przepisy prawne oraz wymagania jednostek samorządu terytorialnego są niejednoznaczne. Kolejnym istotnym problemem jest stosowanie różnego rodzaju dodatków do paliw stałych. Często dodatki te, pomimo wysokich walorów energetycznych, nie powinny zostać poddane procesowi spalania przez indywidualnych użytkowników z powodu warunków technicznych procesu spalania w indywidualnych urządzeniach grzewczych. Z punktu widzenia użytkownika przy obowiązujących uwarunkowaniach prawnych nie ma możliwość zweryfikowania składu paliwa na etapie zakupu. Podjęta w artykule tematyka wskazuje na przyczyny zjawiska i podkreśla potrzeby wdrożenia modelu identyfikacji. W pracy szczegółowo omówiono diagnozę aktualnej sytuacji w zakresie interesariuszy przedsięwzięcia z uwzględnieniem ich potrzeb, oczekiwań przy uwzględnieniu obowiązujących przepisów prawnych. W artykule wskazano możliwości w zakresie potencjalnych technik identyfikacji domieszek w materiałach opałowych, co pozwoli uzyskać skuteczne narzędzie jednoznacznie określające skład i czystość materiału opałowego oraz co istotniejsze produkty ich spalania. Ponadto przeanalizowano techniki umożliwiające weryfikację spalania i/lub współspalania odpadów komunalnych przez indywidualne urządzenia grzewcze, podkreślając wybrane modele koncepcji. W pracy wskazano na istotny element wdrożenia, którym jest ocena skuteczności. Zakłada się, iż z punktu widzenia założonego celu i przeprowadzonej analizy otoczenia wdrożenia zarówno po stronie interesariuszy, jak i wymagań prawnych, zaproponowany model koncepcji będzie skutecznym elementem poprawy jakości powietrza w zakresie eliminacji procederu nielegalnego spalania, termicznego przekształcania odpadów komunalnych przez użytkowników palenisk domowych oraz wskazania, czy paliwo stałe stosowane do spalania nie stanowi mieszaniny paliwa legalnego z dodatkami nieznanego pochodzenia.

Wood pellets are classified as a solid biomass type. They are one of the most popular bio-heating fuels used in Europe, especially in the small heating sector, where pellets are burned in low-power domestic boilers. The pellets and automatic pellet-fired heating devices gained popularity due to the increasing air pollution (smog) problem and the low emission limiting campaigns associated with it. Wood pellets are formed as a result of small forestry particles mechanical compression (mainly conifers originated) and they are listed among renewable energy sources. The purpose of the presented studies was to compare the quality of wood pellets used for pellet-fired boilers and to identify, qualitatively and quantitatively, impurities marked in the samples obtained from the domestic market. The application of petrographic analyses, applied so far in relation to fossil fuels, is a presented work innovation for wood pellets. The microscopic analyses were performed on both certified (ENplus/DINplus) and uncertified wood pellets available on the market. Unfortunately, the analysis revealed that the quality requirements were not met, because of the unacceptable contamination presence. The unacceptable organic inclusions in the analyzed samples are fossil coals and their derivatives, coke, and polymeric materials of natural origin. Unacceptable inorganic inclusions determined in the analyzed samples were: glass, slag, rust, pieces of metal, stone powder, plastic, and polymeric materials of inorganic origin.

Procesy spalania, a w szczególności spalanie węgla kamiennego i brunatnego, stanowią jedno z głównych antropogenicznych źródeł emisji pierwiastków ekotoksycznych do atmosfery. W związku z tym nie tylko emisja gazów cieplarnianych czy pyłów, ale także zanieczyszczenie atmosfery szkodliwymi pierwiastkami potocznie zwanymi „metalami ciężkimi” (takimi jak: rtęć, ołów czy kadm) jest obiektem zaostrzającej się polityki klimatycznej Unii Europejskiej. W artykule dokonano przeglądu i analizy zarówno dotychczas obowiązujących przepisów unijnych, jak i krajowych uregulowań prawnych związanych z emisją pierwiastków ekotoksycznych z procesów spalania paliw stałych. Problematyka ta stała się szczególnie ważna dla przemysłu elektroenergetycznego w kontekście przyjętych przez Komisję Europejską w kwietniu 2017 roku konkluzji BAT dla dużych obiektów energetycznego spalania (LCP). Ponadto zidentyfikowano oraz scharakteryzowano najważniejsze czynniki wpływające na wielkość emisji tych zanieczyszczeń do atmosfery. Na podstawie danych literaturowych oraz badań własnych przeprowadzono analizę zawartości wybranych pierwiastków ekotoksycznych w krajowych węglach. Na podstawie tej analizy podjęto próbę oceny ew. wpływu jakości polskich węgli na sytuację krajowego sektora energetycznego w świetle prowadzonej przez UE polityki środowiskowej. Uzyskane wyniki wskaźników emisji niektórych pierwiastków ekotoksycznych różnią się od wskaźników stosowanych przez KOBiZE do szacowania wielkości emisji. Rodzi to potrzebę ciągłego monitorowania zawartości pierwiastków ekotoksycznych w polskich węglach oraz okresową weryfikację wskaźników emisji tych pierwiastków. Oszacowana średnia wartość emisji rtęci z badanych węgli energetycznych wyniosła 7,8 μg/m3 (0°C; 101,325 kPa). W związku z tym spalanie badanych węgli energetycznych w istniejących instalacjach elektrowni o mocy powyżej 300 MWth może skutkować niespełnieniem wchodzących w życie norm emisji rtęci do atmosfery, a co za tym idzie koniecznością stosowania węgli poddanych wzbogacaniu. Obliczona średnia emisja Hg dla analizowanych w celach porównawczych węgli koksowych poddanych procesowi wzbogacania nie przekracza wartości dopuszczalnych w nowych regulacjach.

In the processes of coal mining, preparation and combustion, the rejects and by-products are generated. These are, among others, the rejects from the coal washing and dry deshaling processes as well as the coal combustion by-products (fly ash and slag). Current legal and industry regulations recommend determining the content of mercury in them. The regulations also define the acceptable content of mercury. The aim of the paper was to determine the mercury content in the rejects derived from the coal cleaning processes as well as in the combustion by-products in respect of their utilization. The mercury content in the representative samples of the rejects derived from the coal washing and dry deshaling processes as well as in the coal combustion by products derived from 8 coal-fired boilers was determined. The mercury content in the rejects from the coal washing process varied from 54 to 245 μg/kg, (the average of 98 μg/kg) and in the rejects from the dry deshaling process it varied from 76 to 310 μg/kg (the average of 148 μg/kg). The mercury content in the fly ash varied from 70 to 1420 μg/kg, (the average of 567 μg/kg) and in the slag it varied from 8 to 58 μg/kg (the average of 21 μg/kg). At the moment, in light of the regulations from the point of view of mercury content in the rejects from the coal preparation processes and in the coal combustion by-products, there are no significant barriers determining the way of their utilization. Nevertheless, in the future, regulations limiting the maximum content of mercury as well as the acceptable amount of leachable mercury may be introduced. Therefore, preparing for this situation by developing other alternative methods of using the rejects and by-products is recommended.

Power production is the largest source of emissions of anthropogenic carbon dioxide. The main fuels in Poland are solid fuels - hard coal and lignite. Their combustion produces large quantities of waste, primarily fly ash. The ashes from lignite, due to the chemical and phase composition, and thus their properties, have - so far - limited economic use. Among their possible applications is the use of mineral sequestration of carbon dioxide - this is the result of their relatively high content of active CaO and MgO, which can react with carbon dioxide in aqueous suspensions. The paper presents maximum theoretical capacity of CO2 bonding for examined fly ashes and the results of the research on absorption of CO2 by the ash-water suspensions from fly ash resulting from the combustion of lignite from Pątnów and Turów power plants. Calculated for the examined fly ashes maximum theoretical capacity of CO2 bonding amounted to 14% for the ashes from Pątnów power plant and 14.4% for the fly ashes from Turów power plant. Studies have shown that most CO2 - 8.15 g/100 g of ash, was absorbed by suspension with ashes from Turów power plant with a mass ratio of ash to water of at 0.8:1. In the case of ash from Pątnów power plant absorption was lower and amounted to a maximum - 8.7 g CO2/100 g ash. The largest increase CO2 absorption was observed in the first 30 minutes of carbonation in the suspensions of fly ash from Pątnów power plant and the first 15 minutes in suspensions of fly ash from Turów power plant. After this time, the absorption has increased slowly. An increase in temperature in the chamber system, confirming the occurrence of the process of carbonation and its endothermic character. The highest temperature - 44.8 C recorded in the suspension with ashes from Turów power plant, which has also the greatest absorption of CO2. The results confirm the usefulness of these ashes to sequester carbon dioxide.

Fly ashes from the combustion of lignite coal are suitable materials for the creation of suspensions in which CO2 is bound by mineral carbonation. Considering their limited economic uses, mineral sequestration, as a stage of the CCS technology in lignite coal power plants, can be a way of recycling them. Mineral sequestration of CO2 was researched using fly ashes from the combustion of lignite coal in the Pątnów power plant, distinguished by a high content of CaO and free CaO. Research into phase composition confirmed the process of carbonation of the whole calcium hydroxide contained in pure suspensions. The degree of CO2 binding was determined on the basis of thermogravimetric analysis. A rise in the content of CaCO3 was found in the suspensions after subjecting them to the effects of carbon dioxide. Following carbonation the pH is lowered. A reduction in the leaching of all pollutants was discovered in the studied ashes. The results obtained were compared to earlier research of ashes from the same power plant but with a different chemical composition. Research confirmed that water suspensions of ashes from the combustion of lignite coal in the Pątnów power plant are distinguished for a high degree of carbonation.

The use of biomass in the energy industry is the consequence of ongoing efforts to replace Energy from fossil fuels with energy from renewable sources. However, due to the diversity of the biomass, its use as a solid fuel generates waste with diverse and unstable chemical composition. Waste from biomass combustion is a raw material with a very diverse composition, even in the case of using only one type of biomass. The content of individual elements in fly ash from the combustion of biomass ranges from zero to tens of percent. This makes it difficult to determine the optimal recovery methods. The ashes from the combustion of biomass are most commonly used in the production of building materials and agriculture. This article presents the elemental composition of the most commonly used biomass fuels. The results of the analysis of elemental composition of fly ashes from the combustion of forest and agricultural biomass in fluidized bed boilers used in the commercial power industry were presented. These ashes are characterized by a high content of calcium (12.3–19.4%), silicon (1.2–8.3%), potassium (0.05–1.46%), chlorine (1.1–6.1%), and iron (0.8–6.5%). The discussed ashes contained no sodium. Aluminum was found only in one of the five ashes. Manganese, chromium, copper, nickel, lead, zinc, sulfur, bismuth, titanium and zirconium were found in all of the examined ashes. The analysis of elemental composition may allow for a preliminary assessment of the recovery potential of a given ash.

Strength and permeability properties along with microstructural evolution of hardened slurries composed of fly ash from fluidal bed combustion of brown coal and an addition of OPC/BFSC is assessed in this paper. An increase in the amount of fly ash in slurries influences the development of mechanical strength and a decrease of hydraulic conductivity. SEM, XRD, and porosity analyses confirmed formation of watertight microstructures. The structure of slurries is composed of ettringite, C-S-H phase, AFt, and AFm phases. Ettringite crystallises as relatively short needles forming compact clusters or intermixed with the C-S-H phase. The occurring C-S-H phases are mainly of type I – fibrous and type II – honeycomb