火电厂大气污染物排放标准之管见

本文将《火电厂大气污染物排放标准》（ＧＢ１３２２３－１９９６）与原《燃煤电厂大气污染物排放标准》（ＧＢ１３２２３－９１）在多方面作了比较，从环保管理者的角度，分析了新标准对电力建设与污染治理产生的影响，对今后在执行新标准的过程中可能遇到的问题提出了一些见解。     

发电集团应对燃煤电厂超低排放的思考

新的《火电厂大气污染排放标准》全面加大了对火电厂大气污染物中烟尘、SO2、NOx的控制力度，收严了污染物排放限值。近期提出的煤电节能减排升级与改造行动计划，进一步提出了燃煤电厂达到燃气机组排放标准的超低排放要求。解读了燃煤电厂推行超低排放的一些政策支撑、技术路线，从华电集团超低排放技术及应用实例出发，对超低排放技术实施过程中需要关注的问题进行了探讨，具有一定的参考价值。     

欧盟国家燃煤电厂环保政策及技术路线分析

温室气体的排放控制作为全球性的环境问题受到了广泛关注。中国是火力发电的大国,其燃煤机组的温室气体排放总量巨大。《火电厂大气污染物排放标准》（GB 13223-2011）提高了我国燃煤电厂的烟气污染物排放的要求,对火电厂烟气处理的技术选择和投资都会产生重大影响。针对中国燃煤电厂环保面临的新形势,阐述了欧盟国家的环保政策重点,并对欧盟国家燃煤电厂污染物控制的相关标准进行了分析,同时简要介绍了欧盟国家燃煤电厂环保的主要技术路线,在一定程度上可作为中国燃煤电厂污染物控制的借鉴和参考。     

内地与香港燃煤电厂大气污染物排放控制政策与标准比较

香港特区与广东省政府联合成立粤港持续发展与环保合作小组,并发表《改善珠江三角洲空气质量的联合声明》（简称＂减排联合声明＂）,同意制定合理的减排方案,共同执行管理计划。总结分析了粤、港地区在治理燃煤电厂大气污染物方面的控制政策,并对大陆与香港特区燃煤电厂大气污染物的排放标准进行比较。     

燃煤电厂汞排放分析及控制技术研究

新的《火电厂大气排放标准》的颁布实施，燃煤电厂汞的排放正式纳入控制标准。针对目前我国燃煤电厂汞排放化学形态转换、排放特征，分析和总结现有污染控制设施对汞协同控制效果，提出适合我国国情的燃煤电厂汞控制技术措施的建议及发展趋势，可有效控制燃煤电厂汞的排放量。     

《火电厂大气污染物排放标准》重新修订实施

为贯彻实施新修订的《火电厂大气污染物排放标》(GB13223-2003)(以下简称《排放标准》)，有效控制火电厂大气污染物排放，2004年5月21日国家环保总局就有关要求通知如下：     

稀土氧化物催化还原烟气中的SO2

在实验室研究结果的基础上，建立了小型实际燃煤烟气脱硫试验装置，采用实际燃煤烟气进行了稀土氧化物催化还原烟气脱硫的试验，考察了空速、反应温度对脱硫率的影响。试验结果表明，在反应温度520～550℃、空速2800h。的条件下，脱硫率为99％，NOx的去除率为95％，SO2最高排放质量浓度为100mg／m^3，NOx最高排放质量浓度为50mg／m^3，符合GB13223-2003《火电厂大气污染物排放标准》2时段标准，与实验室的实验结果基本吻合。     

二个大气污染物排放标准中计算方法比较

就《火电厂大气污染物排标准》（ＧＢ１３２２３－１９９６）和《制定地方大气污染物排放标准的技术方法》（ＧＢ／Ｔ１３２０１－９１）两个国家标准的污染物允许排放量计算公式进行了比较，指出了它们的差异及适用范围。     

燃煤电厂汞排放及其控制技术研究

燃煤电厂汞排放是最大的人为汞污染源,《火电厂大气污染物排放标准》(GB 13223-2011)首次提出了我国燃煤发电锅炉汞及其化合物的控制指标,规定汞及其化合物排放限值为0.03 mg/m3.介绍了国内外汞污染发展情况,汞的形态以及汞污染控制技术.汞控制技术主要分为三种:燃烧前脱汞、燃烧中脱汞和燃烧后脱汞,其中燃烧后脱汞的研究最广泛.     

石油炼制行业新旧污染物排放标准的差异

分别介绍了旧标准GB 8978—1996《污水综合排放标准》、GB 16297—1996《大气污染物综合排放标准》和新标准GB 31570—2015《石油炼制工业污染物排放标准》的核心内容。从适用范围、排放限值和污染控制因子3个方面分析了石油炼制行业新旧污染物排放标准的差异。     

Programs assessing implementation and effectiveness of state forest practice rules and BMPs in the West

The major forest nonpoint source control programs in the West are largely regulatory, either under forest practices acts (California, Idaho, New Mexico, Nevada, Oregon, and Washington) or a streamside management act (Montana). These programs and the specific rules they enforce continue to undergo intensive scrutiny. Still, the questions are the same for these regulatory programs as for states that base nonpoint source control on voluntary BMPs (Arizona, Colorado, Utah, Wyoming). Are the rules or BMPs being applied, and are they effective in reducing nonpoint source pollution to levels that protect beneficial uses of water? The level of debate about forestry in the West has resulted in detailed monitoring and research to answer these questions. In the past, state agencies have assumed levels of BMP compliance based on the percent of operations without enforcement actions. These estimates are being replaced by statistically valid and reproducible monitoring of forest practices rules and BMP compliance levels. BMP effectiveness is being assessed using both qualitative and quantitative methods. This can involve field assessments, process-based research, and control watershed studies. Some trend monitoring is also beginning. With the regional implementation rate for forestry BMPs at about 94% and rising, it is likely that effectiveness testing will continue to be a priority and consume the majority of assessment resources for this region.     

Effect of Coconut, Sisal and Jute Fibers on the Properties of Starch/Gluten/Glycerol Matrix

Coconut, sisal and jute fibers were added as reinforcement materials in a biodegradable polymer matrix comprised of starch/gluten/glycerol. The content of fibers used in the composites varied from 5% to 30% by weight of the total polymers (starch and gluten). Materials were processed in a Haake torque rheometer (120 °C, 50 rpm) for 6 min. The mixtures obtained were molded by heat compression and further characterized. Addition of lignocellulosic fibers in the matrix decreased the water absorption at equilibrium. The diffusion coefficient decreased sharply around 5% fiber concentration, and further fiber additions caused only small variations. The thermogravimetric (TG) analysis revealed improved thermal stability of matrix upon addition of fibers. The Young’s modulus and ultimate tensile strength increased with fiber content in the matrix. The storage modulus increased with increasing fiber content, whereas tanδ curves decreased, confirming the reinforcing effect of the fibers. Morphology of the composites analyzed under the scanning electron microscope (SEM) exhibited good interfacial adhesion between the matrix and the added fibers. Matrix degraded rapidly in compost, and addition of increased amounts of coconut fiber in the matrix caused a slowdown the biodegradability of the matrix. Names are necessary to report factually on available data; however, the USDA neither guarantees nor warrants the standard of the product, and the use of the name by USDA implies no approval of the product to the exclusion of others that may be suitable.     

Quantification of Polymerisation Processes During The Oxidative Degradation of 14C-Labelled Chlorophenols

In experiments employing the lignocellulose-decaying basidiomycetes Trametes versicolor and Stropharia rugosoannulata degrading uniformly¹⁴C-labelled 2,4-dichlorophenol and pentachlorophenol, acombination of size exclusion chromatography (SEC),fractionation, and -scintillation counting wasapplied to quantify polymerisation products formed duringchlorophenol degradation. Time-dependent mass balances weregenerated by analysis of ¹⁴C in polymerisation products,CO₂, as well as monomer non-polar and polar metabolites.Approximately 30% of the chlorophenols were found to bepolymerised. A major fraction of the polymerised productscorresponded to a molecular weight range from 0.24 – 40 kDa.Only a minor fraction could be attributed to a molecularweight >40 kDa. This method proved to be useful inquantification of polymerisation products and kinetics of thepolymerisation processes, whereas UV/Vis detection ofpolymerisation products separated by SEC led to false positiveresults. The SEC-¹⁴C method could also be applied forother complex processes where polymerisation ordepolymerisation occurs (humification, degradation oflignocellulose, formation of bound residues from xenobioticssuch as polycyclic aromatic hydrocarbons or 2,4,6-trinitrotoluene) and where spectrophotometric determinationsare difficult or impossible.     

The Relative Influences of Primary and Secondary Particulates to Urban Air Quality in the United Kingdom

This study uses a combination of data from U.K. monitoringstations and from modelling undertaken with the U.K.Meteorological Office's NAME Model to investigate therelative influences of primary and secondary particulateson total PM₁₀ levels at sites in the United Kingdom. Co-located PM₁₀ and sulphate aerosol measurementsindicate that sulphate has a disproportionately largeinfluence on the variation of PM₁₀ levels incomparison to its contribution to their total mass.Comparisons of measured PM₁₀ at urban centre, roadsideand rural sites suggest that local primary sources havevery little influence on daily mean levels. NAME has beenused to model both primary particles and sulphate aerosolfrom sources across the whole of Europe. The discrepanciesbetween modelled and observed PM₁₀ suggest that coarseparticles, such as windblown dust and resuspended roaddust,may comprise a very large, if not dominant, proportion ofobserved PM₁₀ levels. The apparently minor role ofprimary particles (especially locally-sourced ones) raisesa number of issues regarding the suitability of current U.K.and European legislation to addressing the particle problem.     

Hysteresis in Reversal of Central European Mountain Lakes from Atmospheric Acidification

Extremely high emissions of S and N compounds in Central Europe (both 280 mmol m^-2 yr^-1) declined by 70and 35%, respectively, during the last decade. Decreaseddeposition rates of SO₄ ^-2, NO₃ ^-, and NH₄ ⁺ in the region paralleled emission declines. The reduction in atmospheric inputs of S and N to mountain ecosystemshas resulted in a pronounced reversal of acidification in the Tatra Mountains and Bohemian Forest lakes. Between the 1987–1990and 1997–1999 periods, concentrations of SO₄ ^-2 and NO₃ ^- decreased (average ± standard deviation) by 22±7 and 12±7 mol L^-1, respectively, in theTatra Mountains, and by 19±7 and 15±10 mol L^-1, respectively, in the Bohemian Forest. Their decrease was compensated in part (1) by a decrease in Ca²⁺ + Mg²⁺ (17±7 mol L^-1) and H⁺ (4±6 mol L^-1), and an increase in HCO₃ ^-(10±10 mol L^-1) in the Tatra Mountains lakes, and (2) by a decrease in Al (7±4 mol L^-1), Ca²⁺ + Mg²⁺ (9±6 mol L^-1), and H⁺ (6±5 mol L^-1), in Bohemian Forest lakes. Despite the rapid decline in lake water concentrations of SO₄ ^-2 and NO₃ ^- in response to reduced S and N emissions, their present concentrations in some lakes are higher than predictionsbased on observed concentrations at comparable emission rates during development of acidification. This hysteresis in chemical reversal from acidification has delayed biological recovery of the lakes. The only unequivocal sign of biological recovery hasbeen observed in erné Lake (Bohemian Forest) where a cladoceran species Ceriodaphnia quadrangular has recentlyreached its pre-acidification abundance.     

Reconstruction of Long-Term Changes in Lake water Chemistry,Zooplankton and Benthos of a Small,Acidified High-Mountain Lake: Magic Modelling and Palaeolimnogical Analysis

Starolesnianske pleso is a small and shallow acid lake in the High Tatra Mountains, situated at 2000 m above sea level, on granitic bedrock, with sparse and thin soil cover. When detailed measurements began in the 1980s Starolesnianske pleso had pH below 5 and only one species of cladoceran zooplankton, the ubiquitous Chydorus sphaericusPalaeolimnological investigations show changes in cladoceran zooplankton and chironomid zoobenthic assemblages since about 1920 and a major change in 1970–1980. The dynamic acidification model MAGIC was used to reconstruct changes in water chemistry over the past 150 years. The results from MAGIC agree well with the sediment record; pH levels gradually decreased from 6.5 in the mid-1800s to about 5.6 in 1920 (first response in biota) to below 5.0 by 1970, and concentrations of inorganic aluminium rose dramatically beginning about 1960. In the 1990s the lake water chemistry showed clear signs of reversal in acidification brought about by a major decline in S deposition.     

Changes in Extractability of Cr and Pb in a Polycontaminated Soil After Bioaugmentation With Microbial Producers of Biosurfactants, Organic Acids and Siderophores

Partly because of the low bioavailability of metals, the soil cleaning-up using phytoremediation is usually time-consuming. In order to enhance the amount of metals at the plant's disposal, the soil bioaugmentation coupled together with phytoextraction is an emerging technology. In this preliminary work, two agricultural soils which mainly differed in their Cr, Hg and Pb contents (LC, low-contaminated soil; HC, high-contaminated soil) were bioaugmented in laboratory conditions by either bacterial (Bacillus subtilis, Pseudomonas aeruginosa, Pseudomonas fluorescens or Ralstonia metallidurans) or fungal inocula (Aspergillus niger or Penicillium simplicissimum) and incubated during three weeks. The LC soil pots bioaugmented with A. niger and P. aeruginosa contained higher concentrations of Cr (0.08 and 0.25 mg.kg⁻¹ dw soil) and Pb (0.25 and 0.3 mg.kg⁻¹ dw soil) in the exchangeable fraction F1 (extraction with MgCl₂) by comparison with the non-bioaugmented soil where neither Cr nor Pb was detected. Conversely, immobilization of Cr and Pb in the soil were observed with the other microorganisms. The soil bioaugmentation not only modified the metal speciation for the most easily extractable fractions but also modified the distribution of metals in the other fractions, to a lesser extent nevertheless. The difference in microbial concentrations between the bioaugmented or not HC soils reached up to 1.8 log units. Thus the microorganisms that we chose for the soil bioaugmentation were competitive towards the indigenous microflora. The PCA analysis showed close positive relationships between the microorganisms which potentially produced siderophores in the soil and the amount of Cr and Pb in the fraction F1.     

Heavy Metals Removal by Biosorption and Flotation

The removal of a mixture of heavy (toxic) metal cations (copper, nickeland zinc) from liquid effluents was investigated in this study at pilotscale, using counter-current contact mode. The innovative processinvolved the abstraction of metal ions onto fungal biosorbents, followedby the application of flotation for the subsequent solid/liquid separationof biomass particles. The ability of microorganisms to remove metal ionsfrom aqueous solutions is a well-known phenomenon. Nevertheless,engineering considerations are very important in decisions, concerningthe commercial future of biosorption and practical solutions are neededfor certain problems, such as the efficient post-separation ofmetal-loaded biomass. The two processes (flotation and biosorption) caneffectively operate in combination, in what it was termed biosorptiveflotation process. The sorbents may be recycled, after appropriate elutionof metals, as well as the treated (clean) water.     

酸浸出法回收冶金污泥中的有价金属

采用二次酸浸出的方法回收镍钴湿法冶金工业污泥中的有价金属。先采用水和硫酸作为浸出剂浸出Mg和Na,最佳工艺条件为浸出液的pH 7.5、浸出时间5 min、浸出剂体积与干污泥质量的比(ω)为10 mL/g。再采用硫酸作为浸出剂、焦亚硫酸钠作为还原剂进行二次酸浸,在硫酸与污泥质量比为1.3、焦亚硫酸钠与污泥质量比为0.3、ω为5 mL/g、浸出温度85℃、浸出时间20 min的最佳工艺条件下,Co、Ni、Cu、Mn和Zn的浸出率分别达92.45%、93.48%、89.52%、97.78%和94.79%。经XRD表征,浸出后污泥中未见原污泥中的矿物相,说明原污泥中的矿物几乎全部被溶解。     

不同原料生物炭对NH4+-N、PO43--P吸附性能的差异性及其成因分析

以芦苇、小麦秸秆和竹子为原料,利用回流式炭化工艺制备3种生物炭。比较三者对NH_4~+-N、PO_4~(3-)-P的吸附性能,并对三者吸附性能差异的成因进行分析。实验结果表明:3种生物炭对PO_4~(3-)-P的吸附效果整体上优于NH_4~+-N,因为3种生物炭的阳离子交换容量CEC值和Zeta电位绝对值的水平均较低,不利于阳离子的吸附;竹炭Z-C对NH_4~+-N的吸附效果最佳,6 h去除率为3.59%,低的N含量、pH及Zeta电位绝对值对NH_4~+-N的吸附有利;芦苇炭LW-C中的O更多地与K、Mg等结合,形成能够与PO_4~(3-)反应生成磷酸盐沉淀或者晶体物质的金属氧化物,从而具有最好的PO_4~(3-)-P的吸附效果,6 h时去除率达16.91%。