DEMONSTRATION AND EVALUATION OF PROCESSED FOREST BIOMASS IN BIORETENTION CELLS FOR REDUCTION OF WILDFIRE HAZARD AND TREATMENT OF STORMWATER RUNOFF

S. Templeton, C. Privette, J. Hayes, C. Post, Ritu Sharma
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Widespread use of this structural best management practice could expand the market for small-diameter woody material and might reduce risks of wildfire because processed residues from logging decks could be the source of organic material that the cell requires. The purpose of this project was to demonstrate the use of processed forest biomass in a bioretention cell at an industrial park in a developing area of South Carolina and evaluate the environmental performance and costs of this cell. A bioretention cell, approximately 25’ wide, 75’ long, and 4’ deep with a 12” layer of chipped logging residue, was designed and installed at the Orangeburg County and City Industrial Park. The cell and the use of processed forest biomass in the cell were publicized in a newsletter of the state’s environmental regulatory agency, are publicized by an on-site sign, and will be publicized by a magazine article for Clemson University. Aged chips of woody forest residues remove positive amounts of nitrate nitrogen, zinc, and copper from polluted solutions in laboratory tests, even though the removal efficiencies never exceed the efficiencies of at least one of the two commercial hardwood mulches. This chipped woody material does not add more phosphorous than the two commercial mulches. Although the level of total organic carbon decreases slightly over time as pine chips age, this type of processed forest biomass can serve as an adequate source of carbon for denitrification within the bottom iii chamber of a bioretention cell. In general, the bioretention cell in Orangeburg reduces the quantity of runoff to the existing storm sewer. Ninety four percent of the first inch of runoff enters and is treated by the cell. The cell apparently removes zinc and copper. Although the cell did not always remove phosphate and nitrate, removal of these pollutants improved as time passed. Concentrations of measured pollutants in the discharge were substantially below regulatory thresholds for water quality. The bioretention cell in Orangeburg cost $28,860. The largest portion of these costs was $23,500 for the contractor, his sub-contractor, and their materials. Unusually but justifiably large excavation and grading expense for innovative design, insufficient bid competition, and contractor inexperience are reasons why the costs per unit of water-quality volume were higher in this project than the average of others. Bioretention cells exhibit economies of water-quality size. If the volume of water that a cell treats for pollutants increases by one percent, the total costs of the cell increase by an estimated 0.765 percent in coastal areas of mid-Atlantic states, 0.734 percent in the Piedmont region, and 0.629 percent in the Sandhill region. Hence, costs per unit of water-quality volume decrease as the volume of water that a cell treats for pollutants increases. Regardless of region, a one percent increase in the hourly wage of engineers in the area where a cell is located leads to a 6.69 percent increase in the total costs of the cell. Meaningful comparisons of costs of bioretention cells and stormwater ponds are difficult, if not impossible, to make because stormwater ponds have been designed primarily to reduce stormwater runoff while most bioretention cells have been designed primarily to remove pollutants. Determination of the precise ranges of water-quality volumes and drainage areas over which bioretention cells are cheaper than stormwater ponds to meet regulatory standards for iv quality and quantity of stormwater runoff remains an important question for research. In August 2004 South Carolina had 803 industrial sites and 241 industrial parks that covered 189,605 undeveloped acres. If owners or tenants of these industrial parks and sites eventually develop all of the land, manage stormwater exclusively with bioretention cells, allocate an average of 0.0525 of each developed acre for the surface area of cells, and use one foot of chipped woody material in the cells, they would use 16.06 million yds3 or 4.553 million tons of this material. If the real cost were to remain $22 per delivered ton, then developers of these parks and sites would spend $100.2 million over time to use the material in bioretention cells.","PeriodicalId":338433,"journal":{"name":"The research reports","volume":"1 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2004-10-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"1","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"The research reports","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.22004/AG.ECON.187460","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 1

Abstract

Growth of urban areas and impervious surfaces in the U.S. has increased the environmental impacts of stormwater runoff and the public’s interest in regulation of those who discharge it. Growth of communities in the urban-wildland interface is an important reason why risks of wildfire have increased and government agencies have undertaken new collaborative efforts to reduce them. A bioretention cell is a space-saving method to manage stormwater runoff from streets and parking lots. Widespread use of this structural best management practice could expand the market for small-diameter woody material and might reduce risks of wildfire because processed residues from logging decks could be the source of organic material that the cell requires. The purpose of this project was to demonstrate the use of processed forest biomass in a bioretention cell at an industrial park in a developing area of South Carolina and evaluate the environmental performance and costs of this cell. A bioretention cell, approximately 25’ wide, 75’ long, and 4’ deep with a 12” layer of chipped logging residue, was designed and installed at the Orangeburg County and City Industrial Park. The cell and the use of processed forest biomass in the cell were publicized in a newsletter of the state’s environmental regulatory agency, are publicized by an on-site sign, and will be publicized by a magazine article for Clemson University. Aged chips of woody forest residues remove positive amounts of nitrate nitrogen, zinc, and copper from polluted solutions in laboratory tests, even though the removal efficiencies never exceed the efficiencies of at least one of the two commercial hardwood mulches. This chipped woody material does not add more phosphorous than the two commercial mulches. Although the level of total organic carbon decreases slightly over time as pine chips age, this type of processed forest biomass can serve as an adequate source of carbon for denitrification within the bottom iii chamber of a bioretention cell. In general, the bioretention cell in Orangeburg reduces the quantity of runoff to the existing storm sewer. Ninety four percent of the first inch of runoff enters and is treated by the cell. The cell apparently removes zinc and copper. Although the cell did not always remove phosphate and nitrate, removal of these pollutants improved as time passed. Concentrations of measured pollutants in the discharge were substantially below regulatory thresholds for water quality. The bioretention cell in Orangeburg cost $28,860. The largest portion of these costs was $23,500 for the contractor, his sub-contractor, and their materials. Unusually but justifiably large excavation and grading expense for innovative design, insufficient bid competition, and contractor inexperience are reasons why the costs per unit of water-quality volume were higher in this project than the average of others. Bioretention cells exhibit economies of water-quality size. If the volume of water that a cell treats for pollutants increases by one percent, the total costs of the cell increase by an estimated 0.765 percent in coastal areas of mid-Atlantic states, 0.734 percent in the Piedmont region, and 0.629 percent in the Sandhill region. Hence, costs per unit of water-quality volume decrease as the volume of water that a cell treats for pollutants increases. Regardless of region, a one percent increase in the hourly wage of engineers in the area where a cell is located leads to a 6.69 percent increase in the total costs of the cell. Meaningful comparisons of costs of bioretention cells and stormwater ponds are difficult, if not impossible, to make because stormwater ponds have been designed primarily to reduce stormwater runoff while most bioretention cells have been designed primarily to remove pollutants. Determination of the precise ranges of water-quality volumes and drainage areas over which bioretention cells are cheaper than stormwater ponds to meet regulatory standards for iv quality and quantity of stormwater runoff remains an important question for research. In August 2004 South Carolina had 803 industrial sites and 241 industrial parks that covered 189,605 undeveloped acres. If owners or tenants of these industrial parks and sites eventually develop all of the land, manage stormwater exclusively with bioretention cells, allocate an average of 0.0525 of each developed acre for the surface area of cells, and use one foot of chipped woody material in the cells, they would use 16.06 million yds3 or 4.553 million tons of this material. If the real cost were to remain $22 per delivered ton, then developers of these parks and sites would spend $100.2 million over time to use the material in bioretention cells.
生物保留池中处理过的森林生物量用于减少野火危害和处理雨水径流的论证和评价
在美国,城市地区和不透水地表的增长增加了雨水径流对环境的影响,公众对排放者的监管也越来越感兴趣。城市-荒地交界区社区的增长是野火风险增加的一个重要原因,政府机构采取了新的合作努力来减少野火。生物保留细胞是一种节省空间的方法,用于管理街道和停车场的雨水径流。这种结构最佳管理实践的广泛使用可以扩大小直径木质材料的市场,并可能降低野火的风险,因为伐木甲板上的加工残留物可能是细胞所需的有机材料的来源。该项目的目的是在南卡罗来纳发展中地区的一个工业园区展示在生物保留池中使用加工过的森林生物量,并评估该池的环境性能和成本。在奥兰治堡县和城市工业园区,设计并安装了一个生物保留区,大约25英尺宽,75英尺长,4英尺深,有12英寸的伐木残留物碎片层。这个电池和在电池中使用经过处理的森林生物质在国家环境管理机构的通讯中进行了宣传,在现场的标志中进行了宣传,并将在克莱姆森大学的杂志文章中进行宣传。在实验室测试中,木质森林残留物的老化碎片从污染溶液中去除大量的硝酸盐氮、锌和铜,尽管去除效率从未超过至少两种商用硬木覆盖物中的一种的效率。这种破碎的木质材料并不比两种商业覆盖物添加更多的磷。尽管随着松片的老化,总有机碳水平会随着时间的推移而略有下降,但这种类型的加工森林生物量可以作为生物保留细胞底部室中反硝化的足够碳源。总的来说,奥兰治堡的生物保留池减少了流入现有雨水下水道的径流量。第一英寸的径流的百分之九十进入并由细胞处理。细胞显然会去除锌和铜。虽然细胞并不总是去除磷酸盐和硝酸盐,但随着时间的推移,这些污染物的去除能力有所提高。排放中测量到的污染物浓度大大低于水质的规定阈值。奥兰治堡的生物保留细胞花费了28,860美元。这些费用中最大的一部分是承包商、分包商及其材料的23 500美元。创新设计的挖掘和分级费用异常但合理,投标竞争不足,承包商缺乏经验,这些都是该项目单位水质体积成本高于其他项目平均水平的原因。生物保留细胞表现出水质大小的经济性。如果一个电池处理污染物的水量增加1%,那么在大西洋中部沿海地区,电池的总成本估计会增加0.765%,在皮埃蒙特地区增加0.734%,在沙丘地区增加0.629%。因此,单位水质体积的成本随着细胞处理污染物的水量的增加而降低。无论在哪个地区,电池所在地区工程师的时薪每增加1%,电池的总成本就会增加6.69%。要对生物滞留池和雨水池的成本进行有意义的比较是很困难的,如果不是不可能的话,因为雨水池的设计主要是为了减少雨水径流,而大多数生物滞留池的设计主要是为了去除污染物。确定水质容量的精确范围和排水区域,在该范围内生物保留池比雨水池更便宜,以满足雨水径流的质量和数量的监管标准,仍然是一个重要的研究问题。2004年8月,南卡罗来纳州有803个工业基地和241个工业园区,占地189,605英亩。如果这些工业园区和场地的所有者或租户最终开发所有的土地,只使用生物保留细胞来管理雨水,平均每开发英亩分配0.0525的细胞表面积,并在细胞中使用一英尺的木屑材料,他们将使用1606万码3或455.3万吨这种材料。如果实际成本保持在每交付吨22美元,那么这些公园和场地的开发商将花费1.002亿美元用于在生物保留细胞中使用这种材料。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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