type Volume loading Hydraulic load (filtration rate) Hydraulic retention time of empty bed Carbon oxidation filter 3.0~6.0kgBOD5/(m·d) 2.0~10.0 m/(m·h) 40~60min Nitrifying filter 3.0~6.0NH3-N/(m·d) 3.0~12.0 m/(m·h) 30~45min Denitrification biofilter 3.0~6.0kgNO3-N/(m·d) 6.0~12.0 m/(m·h) 20~30min Carbon oxidation / nitrification filter 1.0~3.0kgBOD5/(m·d)
0.4~0.6kgNH3-N/(m·d)
1.5~3.5 m/(m·h) 80~100min Pre denitrification biofilter 0.8~1.2kgNO3-N/(m·d) 8.0~10.0 m/(m·h) 20~30min Post denitrification biofilte 1.5~3.0kgNO3-N/(m·d) 8.0~12.0 m/(m·h) 20~30min

 

matters needing attention:

 

1. The dissolved oxygen in the effluent of carbon oxidation filter and nitrification filter should be controlled at 3.0 ~ 4.0mg/l.

 

2. The increase of filtration rate is disadvantageous to carbon oxidation, and some non dissolved organic matters are discharged for degradation, 6m / h is recommended.

 

3. However, in a certain volume load range, the increase of filtration rate will not reduce the removal rate of BAF, but also increase the nitrification and denitrification efficiency. The main reasons are as follows: 1. High filtration rate enhances the mass transfer efficiency in the filter, which makes more opportunities for contact between air, sewage and organisms; 2. Under high filtration rate, the biofilm renews rapidly and enhances the biological activity. 3、 At low speed, the filter material is easy to block, which shortens the backwashing cycle, while frequent backwashing is unfavorable to the nitrifying bacteria with slow propagation speed.

 

4. When the filter is mainly used for carbon oxidation, when the required BOD5 is 10-20mg / L, the recommended volume load is 3.5-5.0kg BOD5 / (m · d), when the required BOD5 is 5-10mg / L, the recommended volume load is 2.5-3.2kg BOD5 / (m · d).

 

5. When the filter is mainly used for carbon oxidation and nitrification, the volume load of BOD5 is recommended to be ≤ 3.0kgbod5 / (m · d). The study shows that when the volume load of BOD5 is greater than this value, the removal of ammonia nitrogen is inhibited, and when the volume load of BOD5 is ≥ 4.0kgbod5 / (m · d), the removal of ammonia nitrogen is obviously inhibited.

 

6. The effluent CODcr is 60 mg / L, and the influent load should be 4.0-5.0 kgcodcr / (m · d). When CODcr ≤ 50 mg / L, the influent load should be controlled below 3.0 kgcodcr / (m · d).

 

7. When there are nitrification and denitrification requirements in the filter, the volume load of nitrification and denitrification needs to be calculated. It is recommended that the volume load be less than 2.0kg NH3-N / (m · d) and 5.0kg NO3-N / (m · d) respectively, and 0.3-0.8kg NH3-N / (m · d) and 0.8-4.0kg NO3-N / (m · d) are recommended.

 

8. When denitrification is needed and the carbon source is insufficient, the denitrification tank can be placed in front of the nitrification tank, and part of the effluent from the nitrification tank can be returned to the denitrification tank to form pre denitrification. It has the following advantages: A. use the organic matter in the sewage as the carbon source to reduce the external carbon source. b. Organic matter is removed in the denitrification tank to ensure the nitrification capacity in the carbon oxidation / nitrification tank. c. The aeration capacity of the system is relatively small. d. Less sludge. For the domestic sewage with sufficient BOD5 and nitrogen removal, the advantages of pre denitrification process are obvious considering the operation cost.

 

9. The post denitrification process is more suitable for the following places: A. wastewater with significantly lower BOD5 content (high proportion of industrial wastewater). b. When it is used in the renovation and upgrading of the sewage plant, the nitrification index is not considered before. The BOD5 of the effluent is low, but the ammonia nitrogen is high.

 

10. In order to avoid the influence of carbon removal on nitrification, the post denitrification should be carried out in the pre-treatment stage to remove a part of BOD5. The design filtration rate of C / N tank is 6-10m / h, and the nitrification load should meet the following requirements: inlet BOD5 ≥ 60mg / L, about 0.3KG NH3-N / (m · d), when BOD5 = 20-50mg / L, about 0.6kg NH3-N / (m · d), when BOD5 ≤ 20mg / L, about 1.0kg NH3-N / (m · d), if methanol is used as the external carbon source, then DN is added The amount is 3.3kgch4o/kgno3-n.

 

11. The recommended denitrification load is 0.4-0.5 kgno3-n / (m · d), filtration rate ≥ 10 m / h, and the best influent BOD5 / NO3-N ≥ 6. Generally, the removal rate of BOD5 in DN tank is ≤ 60%, and the removal rate of CODCr is ≤ 70%. The remaining CODcr will enter the nitrification reactor. In order to ensure the nitrification capacity of N tank (greater than 0.5kgnh3-n / (m · d)), the load of CODCr is ≤ 2.0kgcodcr / (m · d). 

Filler type Plate thickness
mm
Theoretical plate number
m
3
Specific surface area
m²/m³
Voidage
m²/m³
Pressure dropMPa/m³ Accumulation weightkg/m³ Liquid loading
m³/m².hm
Maximum f factor-1
m/s(kg/m3)
SB-125Y 1.5-2.0 55 125 0.985 2X10m-1 37.5 0.20-100 3
SB-250Y 0.8-1.0 65 250 0.97 3X10m-1 39.5 0.20-100 2.6
SB-350Y 0.4-0.5 85 350 0.94 2X10m-1 41.5 0.20-100 2
SB-500Y 0.23-0.3 125 500 0.93 3X10m-1 65 0.20-100 1.8
SB-125X 1.5-2.0 45 125 0.985 1.4X10m-1 37.5 0.20-100 3.5
SB-250X 0.8-1.0 55 250 0.97 1.8X10m-1 39.5 0.20-100 2.8
SB-350X 0.4-0.5 75 350 0.94 1.3X10m-1 41.5 0.20-100 2.2
SB-500X 0.23-0.3 115 500 0.93 1.8X10m-1 65 0.20-100 2

 

 

 

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强力海洋生物水产养殖填料

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产品介绍

     概述

    结构包括池体,填料,布水装置,曝气装置。工作原理为:在曝气池中设置填料,将其作为生物膜的载体。待处理的废水经充氧后以一定流速流经填料,与生物膜接触,生物膜与悬浮的活性污泥共同作用,达到净化废水的作用。      

    1、滤料的要求

    (1)比表面积大(2)孔率高(3)质材强度高(4)稳定(5)价格合理

    2、池壁的功能

    构筑物主体,起支撑作用。

    3、池底 通风系统、排泥系统、支承渗水结构

    4、布水系统 旋转布水器

     性能特点:

    1)生物滤池的处理效果非常好,在任何季节都能满足各地最严格的环保要求。

    2)不产生二次污染。

    3)微生物能够依靠填料中的有机质生长,无须另外投加营养剂。因此停工后再使用启动速度快,周末停机或停工1至2周后再启动能立即达到很好的处理效果,几小时后就能达到最佳处理效果。停止运行3至4周再启动立即有很好的处理效果,几天内恢复最佳的处理效果。

    4)生物滤池缓冲容量大,能自动调节浓度高峰使微生物始终正常工作,耐冲击负荷的能力强。

    5)运行采用全自动控制,非常稳定,无须人工操作。易损部件少,维护管理非常简单,基本可以实现无人管理,工人只需巡视是否有机器发生故障。

    6)生物滤池的池体采用组装式,便于运输和安装;在增加处理容量时只需添加组件,易于实施;也便于气 源分散条件下的分别处理。

    7)此类过滤形式的生物滤池能耗非常低,在运行半年之后滤池的压力损失也只有500Pa左右。

     工艺流程:

    1、主要去除污水中含碳有机物时,宜采用单级碳氧化曝气生物滤池;

    2、要求去除污水中含碳有机物并完成氨氮的硝化时,可采用单级碳氧化曝气生物滤池,并适当降低负荷;也可以采用碳氧化滤池和硝化曝气滤池的两级串联工艺;

    3、当进水碳源充足且出水水质对总氮要求高时,宜采用前置反硝化滤池+硝化滤池组合工艺;

    4、当进水的总氮浓度高、碳源不足而出水有对总氮要求严格时,可采用後置硝化工艺,并补充碳源;或采用前置反硝化滤池并外加碳源,前置反硝化滤池的硝化液回流率可具体根据设计NO3-N去除率以及进水碳氮比确定,外加碳源的投加量需经计算后确定。

     

     设计参数

    种类 容积负荷 水力负荷(滤速) 空床水力停留时间
    碳氧化滤池 3.0~6.0kgBOD5/(m·d) 2.0~10.0 m/(m·h) 40~60min
    硝化滤池 3.0~6.0NH3-N/(m·d) 3.0~12.0 m/(m·h) 30~45min
    反硝化生物滤池 3.0~6.0kgNO3-N/(m·d) 6.0~12.0 m/(m·h) 20~30min
    碳氧化/硝化滤池 1.0~3.0kgBOD5/(m·d)
    0.4~0.6kgNH3-N/(m·d)
    1.5~3.5 m/(m·h) 80~100min
    前置反硝化生物滤池 0.8~1.2kgNO3-N/(m·d) 8.0~10.0 m/(m·h) 20~30min
    后置反硝化生物滤池 1.5~3.0kgNO3-N/(m·d) 8.0~12.0 m/(m·h) 20~30min

     

     注意事项:

    1、碳氧化滤池与硝化滤池的出水中的溶解氧宜控制为3.0~4.0mg/L。

    2、滤速增加对碳氧化不利,部分非溶解性有机物为降解就排出,推荐6m/h。

    3、但在一定的容积负荷范围内,滤速增加不但不会降低曝气生物滤池的去除率,还会增加硝化反硝化效率。主要原因有三:一、高滤速增强了滤池内部的传质效率,使得空气、污水、生物之间有更多的接触机会;二、高滤速下,生物膜更新较快,增强了生物的活性。三、低速下,滤料容易堵塞,使得反冲洗的周期缩短,而频繁的反冲洗对繁殖速度较慢的硝化细菌即为不利。

    4、滤池主要用於碳氧化时,当要求出水的BOD5=10~20mg/L,容积负荷推荐采用3.5~5.0kgBOD5/(m‧d),当要求出水的BOD5=5~10mg/L,容积负荷推荐采用2.5~3.2kgBOD5/(m‧d)。

    5、滤池主要用於碳氧化和硝化时,容积负荷建议BOD5≦3.0kgBOD5/(m‧d),研究表明,当BOD5容积负荷大於该值时,氨氮的去除收到抑制,当BOD5≧4.0kgBOD5/(m‧d),氨氮去除收到明显抑制。

    6、出水CODcr在60mg/L,进水负荷应该在4.0~5.0 kgCODcr/(m‧d),当CODcr≦50mg/L,进水负荷应该控制在3.0kgCODcr/(m‧d)以下。

    7、滤池有硝化和反硝化脱氮要求时,需要核算硝化和反硝化的容积负荷。建议容积负荷分别小於2.0kgNH3-N/(m‧d)和5.0 kgNO3-N/(m‧d),推荐采用0.3~0.8kgNH3-N/(m‧d)和0.8~4.0kgNO3-N/(m‧d)。

    8、当需要脱氮,且碳源不足时,可将反硝化池置於硝化池之前,将硝化池部分出水回流到反硝化池,做成前置反硝化。有如下优点:a、利用污水中的有机物作为碳源,减少外加碳源。b、有机质在反硝化池中去除,确保了碳氧化/硝化池中的硝化能力。c、系统的曝气量相对较少。 d、污泥量较少。对於BOD5充足且需脱氮的生活污水,从运行成本考虑前置反硝化工艺优势明显。

    9、后置反硝化工艺更适合用在以下场所:a、BOD5含量明显偏低的废水(工业废水比重高)。b、用於污水厂改造升级,之前未考虑硝化指标,出水BOD5偏低,但氨氮较高。

    10、为避免除碳对硝化的影响,後置反硝化应在预处理阶段,除去一部分的BOD5,C/N池设计滤速6~10m/h 为宜,硝化负荷应满足:进水BOD5≧60mg/L,约为0.3kgNH3-N/(m‧d),当BOD5=20~50mg/L,约为0.6kgNH3-N /(m‧d),当BOD5≦20mg/L,约为1.0kgNH3-N/(m‧d),若以甲醇为外加碳源,则DN投加量为3.3kgCH4O/ kgNO3-N。

    11、设计推荐反硝化负荷0.4~0.5 kgNO3-N/(m‧d),滤速≧10m/h,最好进水BOD5/NO3-N≧6,通常DN池对BOD5的去除率≦60%,对CODcr的去除率 ≦70%,剩馀的CODcr会进入硝化反应器,为确保N池的硝化能力(大於0.5kgNH3-N/(m‧d)),CODcr的负荷≦2.0kgCODcr /(m‧d)。

     生物填料规格

     

    填料型号 板数厚度
    mm
    理论板数
    m
    3
    比表面积
    m²/m³
    空隙率
    m²/m³
    压力降MPa/m³ 堆积重量kg/m³ 液体负荷
    m³/m².hm
    最大F因子-1
    m/s(kg/m3)
    SB-125Y 1.5-2.0 55 125 0.985 2X10m-1 37.5 0.20-100 3
    SB-250Y 0.8-1.0 65 250 0.97 3X10m-1 39.5 0.20-100 2.6
    SB-350Y 0.4-0.5 85 350 0.94 2X10m-1 41.5 0.20-100 2
    SB-500Y 0.23-0.3 125 500 0.93 3X10m-1 65 0.20-100 1.8
    SB-125X 1.5-2.0 45 125 0.985 1.4X10m-1 37.5 0.20-100 3.5
    SB-250X 0.8-1.0 55 250 0.97 1.8X10m-1 39.5 0.20-100 2.8
    SB-350X 0.4-0.5 75 350 0.94 1.3X10m-1 41.5 0.20-100 2.2
    SB-500X 0.23-0.3 115 500 0.93 1.8X10m-1 65 0.20-100 2

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