Research Areas

 Environmental 

 Geotechnical 

 Structures and Materials

Civil Engineering Graduate Seminar Series

* For the previous seminars please visit the research groups' pages

Coming Up!

4 March 2013,  12:10-1 PM, Gregg

Exploring Comparative Performance of Full-Scale, Deep-Bed Anthracite and GAC Biofilters for Simultaneous Removal of Organic Precursors and Manganese

 

Assessing Biological Removal of Manganese 

Presenter: Ransom Horner-Richardson

Advisor: Dr. M.R. Collins

 

Presenter : Varouna Appiah

Advisor: Dr.  M. R. COLLINS

 

Bio: Ransom Horner-Richardson completed his Bachelors of Science in Civil Engineering in May 2012 at the University of New Hampshire. His interest in environmental engineering topics and drinking water treatment in particular, has led him to pursue his Masters degree in the field of Environmental Engineering.  

 

Bio: Varouna obtained her BS in Environmental Engineering, Municipal Processes from UNH in May 2012. She is now pursuing her MS in Civil Engineering (Environmental Engineering track). 

Ransom with Sampling Apparatus in GAC Filter Bed


  

 

 

Abstract: 

Manchester Water-Works Drinking Water Treatment Plant (MWTP) in Manchester, NH operates eight deep bed biofilters following intermediate ozonation for organic precursor removal. Four of the beds use Granular Activated Carbon (GAC) as the filter media and four use crushed anthracite. In the summer months, manganese is prevalent in the source water for MWTP with levels up to 0.25 mg/l. The plant operates the biofilters during these Mn spikes at an elevated pH (8.0) to improve the filter performance for Mn while reducing performance for organic precursors.

This study proposes to assess each deep-bed filter media for differences and similarities in operation and removals for organics and manganese and answer the following questions:

1)      What is the comparative performance of each media type (GAC and anthracite) as a biological growth media for organic precursor (TOC, DOC, BDOC, UV absorbance, SUVA) removal over selected filter cycles (and in particular after filter cleaning) and with regard to filter depth and temperature?

2)      What is the comparative performance of each media type (GAC and anthracite) as a biological manganese (Mn) removal media over selected filter cycles (and in particular after filter cleaning) and with regard to filter depth and temperature?

3)      What is the rate limiting nutrient (RLN) for the biofilters e.g., carbon, nitrogen, phosphorus?

4)      What is the comparative performance of the filters for competing filtration removal goals i.e., organic precursor removals vs. Mn removals, with regard to temperature fluctuation, pH fluctuation, and filter media type?

Each filter type will be assessed over a year cycle to determine the effects of temperature, media type and filter depth on these competing removal goals.

 

Abstract:

Manganese is considered as a secondary contaminant by the US EPA. Therefore, its presence in water is not considered to affect health at the secondary maximum contaminant level (SMCL) of 0.05 mg/L. However, if this level is exceeded in the distribution system, numerous aesthetic problems can be experienced. Indeed, as the water travels through the system, manganese starts to collect as a black manganese oxide biological layer on pipe surfaces causing technical problems. As this layer disperses through the water, consumers may experience undesirable taste and odor.

The most common processes that are used today for manganese removal involve aeration or chemical oxidation followed by filtration. However, biological removal of manganese could provide for a more robust alternative as the MnO2 precipitates resulting from such treatment have stronger configurations than those created by physical-chemical processes. Moreover, the dense biomass formed extends the duration of the filter as head loss increases at a comparatively slower rate. The factors that favor biological removal include redox potential (Eh), dissolved oxygen (DO) concentration, manganese concentration, pH, temperature, and distribution of media.

Spring 2013 Schedule

Date

Time Slot

Name

Advisor

1st or 2nd seminar

Location

Jan 28

12:10-12:35

Georgian Tutuianu

Medina

1st

Kings

12:35-1:00

Patrick Santoso

Goodspeed

1st

Feb 4

12:10-12:35

Jon Coulp-Yu

Bell

1st

Kings

12:35-1:00

Michael Sudak

Benoit

1st

Feb 11

12:10-12:35

Josh Collins

Malley

1st

Gregg

12:35-1:00

RaeAnna Hughes

Malley

1st

Feb 18

12:10-12:35

Jeff Senders

Collins

2nd

Gregg

12:35-1:00

Margaret King

Kinner

1st

Feb 25

12:10-12:35

Jon Coulp-Yu

Bell

2nd

Kings

12:35-1:00

Jennifer Jencks

Kinner

1st

Mar 4

12:10-12:35

Ransom Horne-Richardson

Collins

1st

Gregg

12:35-1:00

Varouna Appiah

Collins

1st

Mar 18

12:10-12:35

Jennifer Jencks

Kinner

2nd

Gregg

12:35-1:00

Margaret King

Kinner

2nd

Mar 25

12:10-12:35

Annika Mathiasson

Medina

2nd

Kings

12:35-1:00

Georgian Tutuianu

Medina

2nd

Apr 1

12:10-12:35

Patrick Santoso

Goodspeed

2nd

Kings

12:35-1:00

David Salzer

Goodspeed

2nd

Apr 8

12:10-12:35

Amy Getchell

Benoit

2nd

Kings

12:35-1:00

Heidi Borchers

Ballestero

1st

Apr 15

12:10-12:35

Bryan Carignan

Jacobs

2nd

Kings

12:35-1:00

Zachary Scanlon

Gress

1st

Apr 22

12:10-12:35

Marc Gullison

Benoit

2nd

Kings

12:35-1:00

Charles Watkins

Kinner

1st

Apr 29

12:10-12:35

Josh Collins

Malley

2nd

Gregg

12:35-1:00

RaeAnna Hughes

Malley

2nd

May 6

12:10-12:35

Rowen Prescott

Goodspeed

2nd

Kings

12:35-1:00

Michael Sudak

Benoit

2nd