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Evaluation of the subsurface vegetated bed form of constructed wetlands for domestic wastewater treatment.

机译:评价用于生活污水的人工湿地的地下植被床形式。

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Sixteen small scale Subsurface vegetated beds (SVB) were installed down slope of the residence at the Whitethorne Planation (WP) site. Treatments included three detention times (2.6, 3.9, and 5.9 days), two recirculation ratios (0 and 0.5), and two plant species (woolgrass (Scirpus cyperinus) and cattail (Typha latifolia)). Twelve larger scale SVBs were constructed at the Powell River Project (PRP) site, Wise County, VA. Treatment consisted of three detention times (4, 8, 12 days) with the same plant species (cattail and woolgrass).; At the WP site, pollutant removal increased with detention time for 5-day biochemical oxygen demand (BOD{dollar}sb5),{dollar} total Kjeldahl nitrogen (TKN), ammonium (NH{dollar}sb4{dollar}-N), phosphates (PO{dollar}sb4sp{lcub}3-{rcub}{dollar}-P), redox potential (Eh), and total dissolved solids (TDS). The pollutant removal rates, based on 23 data sets, were: BOD{dollar}sb5{dollar} (54-70%); NH{dollar}sb4sp+{dollar}-N (30-61%); TKN (33-52%); PO{dollar}sb4sp{lcub}3-{rcub}{dollar}-P (7-28%); fecal coliforms (FC) ({dollar}>{dollar}99%) and coliphages ({dollar}>{dollar}95%). Recirculation appeared to have no apparent benefit. There were no differences in P, S and secondary and trace metals concentrations in the SVBs planted to cattail and woolgrass. Plants could remove 2-10% of the total N applied and 13-57% of the total P applied to the SVBs if harvested once a year during the growing season.; At the PRP site, differences were observed among the detention times for BOD{dollar}sb5,{dollar} TKN, NH{dollar}sb4{dollar}-N, PO{dollar}sb4{dollar}-P, TDS, pH, EC and Eh. The pollutant removal percentages were: FC ({dollar}>{dollar}99%); BOD{dollar}sb5{dollar} (30-75%); NH{dollar}sb4sp+{dollar}-N (27-88%); TKN (27-81%); PO{dollar}sb4sp{lcub}3-{rcub}{dollar}-P (24-46%); and TDS (12-73%). Samples collected from shallow wastewater column exhibited a higher level of treatment. There were no differences in FC, BOD{dollar}sb5,{dollar} TKN and NH{dollar}sb4sp+{dollar}-N concentrations between SVBs planted to cattail and woolgrass, and there were no differences in tissue N content between cattail and woolgrass at both sites.; The average NH{dollar}sb3{dollar} volatilization rate was 236 mg N/m{dollar}sp2{dollar}/day, and accounted for 7-37% of total N applied to the SVBs. Average measured denitrification rates ranged from 3.87 to 6.69 mg N{dollar}sb2{dollar}O/m{dollar}sp2{dollar}/h, and accounted for 2-17% of total N applied.
机译:在Whitethorne Planation(WP)工地的住宅坡下安装了16个小型地下植被床(SVB)。处理包括三个滞留时间(2.6天,3.9天和5.9天),两个循环比(0和0.5天)和两个植物种类(柳桉(Scirpus cyperinus)和香蒲(Typha latifolia))。在弗吉尼亚州怀斯县的鲍威尔河项目(PRP)现场建造了十二个更大的SVB。处理包括相同植物种类(香蒲和羊毛草)的三个滞留时间(4、8、12天)。在可湿性粉剂现场,随着5天生化需氧量(BOD {dollar} sb5),凯氏总氮(TKN),铵盐(NH {dollar} sb4 {dollar} -N),滞留时间的延长,污染物去除量增加,磷酸盐(PO {dollar} sb4sp {lcub} 3- {rcub} {dollar} -P),氧化还原电势(Eh)和总溶解固体(TDS)。根据23个数据集得出的污染物去除率为:BOD {dollar} sb5 {dollar}(54-70%); NH {dollar} sb4sp + {dollar} -N(30-61%); TKN(33-52%); PO {dollar} sb4sp {lcub} 3- {rcub} {dollar} -P(7-28%);粪大肠菌群(FC)({dollar}> {dollar} 99%)和大肠菌群({dollar}> {dollar} 95%)。再循环似乎没有明显的益处。香蒲和羊毛草种植的SVB中的P,S以及次要金属和痕量金属的浓度没有差异。如果在生长季节每年收获一次,则植物可以去除施用给SVB的全部N的2-10%和全部P的13-57%。在PRP网站上,BOD {dollar} sb5,{dollar} TKN,NH {dollar} sb4 {dollar} -N,PO {dollar} sb4 {dollar} -P,TDS,pH, EC和Eh。污染物去除百分比为:FC({dollar}> {dollar} 99%); BOD {dollar} sb5 {dollar}(30-75%); NH {dollar} sb4sp + {dollar} -N(27-88%); TKN(27-81%); PO {dollar} sb4sp {lcub} 3- {rcub} {dollar} -P(24-46%);和TDS(12-73%)。从浅层废水塔收集的样品显示出更高的处理水平。香蒲和羊毛草种植的SVB之间的FC,BOD {dollar} sb5,{dollar} TKN和NH {dollar} sb4sp + {dollar} -N浓度没有差异,并且香蒲和羊毛草的组织氮含量也没有差异。在两个站点上。 NH {dollar} sb3 {dollar}的平均挥发速率为236 mg N / m {dollar} sp2 {dollar} /天,占施用于SVB的总N的7-37%。平均测得的反硝化速率为3.87到6.69 mg N {dollar} sb2 {dollar} O / m {dollar} sp2 {dollar} / h,占施氮总量的2-17%。

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