Fundamental Concepts: Sedimentation

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Fundamental Concepts: Sedimentation Ann Kenimer Texas A & M University University Curriculum Development for Decentralized Wastewater Management

NDWRCDP Disclaimer This work was supported by the National Decentralized Water Resources Capacity Development Project (NDWRCDP) with funding provided by the U.S. Environmental Protection Agency through a Cooperative Agreement (EPA No. CR827881-01 01-0) 0) with Washington University in St. Louis. These materials have not been reviewed by the U.S. Environmental Protection Agency. These materials have been reviewed by representatives of the NDWRCDP. The contents of these materials do not necessarily reflect the views and policies of the NDWRCDP, Washington University, or the U.S. Environmental Protection Agency, nor does the mention of trade names or commercial products constitute their endorsement or recommendation for use.

CIDWT/University Disclaimer These materials are the collective effort of individuals from academic, regulatory, and private sectors of the onsite/decentralized wastewater industry. These materials have been peer-reviewed reviewed and represent the current state of knowledge/science in this field. They were developed through a series of writing and review meetings with the goal of formulating a consensus on the materials presented. These materials do not necessarily reflect the views and policies of University of Arkansas, and/or the Consortium of Institutes for Decentralized Wastewater Treatment (CIDWT). The mention of trade names or commercial products does not constitute an endorsement or recommendation for use from these individuals or entities, nor does it constitute criticism for similar ones not mentioned.

Citation Kenimer, Ann L., J. Villeneuve and S. Shelden. 2005. Fundamental Concepts: Sedimentation - Power Point Presentation. in (M.A. Gross and N.E. Deal, eds.) University Curriculum Development for Decentralized Wastewater Management. National Decentralized Water Resources Capacity Development Project. University of Arkansas, Fayetteville, AR.

Sedimentation Sedimentation is the gravitational accumulation of solids at the bottom of a fluid (air or water)

Types of Settling Four types of sedimentation: Discrete settling Flocculant settling Hindered settling Compression

Examples of Settling Types Discrete Flocculant Hindered

Types of Sedimentation In discrete settling individual particles settle independently It occurs when there is a relatively low solids concentration

Types of Sedimentation In flocculant settling,, individual particles stick together into clumps called flocs This occurs when there is a greater solids concentration and chemical or biological reactions alter particle surfaces to enhance attachment

Types of Sedimentation In hindered settling, particle concentration is great enough to inhibit water movement Water must move in spaces between particles

Types of Sedimentation Compression settling occurs when particles settle by compressing the mass below

Stoke s Law Sedimentation Rate Used for spherical particles Assumes no fluid mixing, so usually will not work for gasses v p = ( ρ ρw ) d p 18µ 2 g

Sedimentation Rate v p = 2 ( ρ ρ ) d g p 18 v p = particle settling velocity ( m / s or ft / s ) ρ p = particle density ( kg / m 3 or lb / ft 3) ρ w = fluid density ( kg / m 3) d = particle diameter (m or ft) g = gravitational acceleration (9.81 m / s 2 or 32.2 ft / s 2) µ = dynamic viscosity (Ns/m 2 or lbs/ft 2 ) w µ

Applications Stoke s Law can be used to determine the surface area of a settling tank Set the critical velocity equal to the settling velocity of the smallest particle The overflow rate is equal to the flow rate into the tank divided by the surface area Setting the overflow rate equal to the critical settling velocity allows time to capture smallest particles of interest

Applications OFR = v = c Q A OFR = over flow rate ( m / s or ft / s ) v c = critical settling velocity ( m / s or ft / s ) Q Q = the flow rate into the basin ( m3 / s or cfs) A A = the surface area of the basin (m 2 or ft 2 )