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CALCULATED BIOSOLIDS� APPLICATION IN THE CHESAPEAKE �BAY WATERSHEDS

Brooke Kline​, Emily Majcher, & Andrew Seckellick

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ABOUT ME

SCHOOL

Rising senior at Saint Mary’s University of Minnesota.

INTERNSHIP

Combined chemistry and environmental science.

A new and different environment.

ACADEMICS

Major: Chemistry and Environmental Biology

Graduating May 2024

POST-GRADUATION

Work for a few years then go back to school

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PER- AND POLYFLUOROALKYL SUBSTANCES (PFAS)

ORIGIN

Used to make products that resist heat, oil, water, and stains (MABA, 2022).

Clothing, cookware, and aqueous film forming foam (AFFF) (Buck and others, 2011).

MOBILITY

They do not break down in the environment (Kleinfelder, 2022).

Are able to move through soil into ground waters (MABA, 2022).

WWTPS

Do not treat for PFAS and end up in the biosolids (Wang and others, 2019).

Solid wastes from septage and other organic matter (do Carmo Precci Lopes and others, 2022).

STRUCTURE

Short chain move rapidly and are more soluble in water (ITRC, 2022).

Long chain are less mobile and more likely to be in soils (ITRC, 2022).

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(Blake and Fenton, 2020)

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MY WORK

WHERE

USGS WSC in MD​

WHY

There is a presence of PFAS in the Chesapeake Bay

WWTPs produce biosolids which are used as a nitrogen fertilizer and are known to contain PFAS

Little is known about the fate of the PFAS from biosolids in the Chesapeake Bay watershed

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OBJECTIVES

Estimate biosolids applied in Chesapeake Bay watershed and create maps as the first steppingstone

Identify areas with the potential for elevated PFAS

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PROJECT METHODS

Literature review of Biosolids 

Gathered and reviewed literature to find PFAS concentration ranges in biosolids

Calculated an estimate of biosolids land applied in 2022 and 2002 in CB watershed from CAST (Chesapeake assessment scenario tool)N in biosolids applied by county

Created maps using R Studio

ACTIVITIES

Assisted with laboratory sampling and analysis for ongoing experiments

Went out into the field to take ground water samples at agricultural sites

Learned coding with R Studio to combine data to produce multiple graphs

Drafted a project plan that outlined the objectives and relevance to why my project is important

Visited EPA CBP office to connect with other and gather different data to be mapped

Attended meetings and presenting to the TCW in August

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THEORETICAL PFAS

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1000 kg = 1 metric ton

1 kg = 1000 g

1000000000 ng=1 g

Literature Concentrations of PFAS in Municipal Biosolids ng of PFAS per gram of biosolids (ng/g)

Sources

Gravesen and others, 2023

Sepulvado and others, 2011

Venkatesan and Halden, 2013

Johnson, 2022

Schultz and others, 2006

Range

Range

Range

Average

Range

PFOS

5.6-803.8

80-219

308-618

12

81-160

PFOA

4.9-352.6

6-68

11.8-70.3

0.44

<3

Total PFAS*

530-3500

*Total of 48 PFAS compounds

ESTIMATED BIOSOLIDS APPLIED BY STATES 

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NEXT STEPS

  • Watershed maps
  • Identify overlap with disadvantaged communities
  • Prioritize investigation of priority watersheds
  • Emerging contaminates in small disadvantaged communities (ES-SDC)

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COMPETENCIES

CIVIC RESPONSIBILITY

Providing a framework for the use of biosolids throughout the watershed and the potential for those biosolids to contain PFAS

ETHICAL REASONING

PFAS in biosolids are not well understood in the watershed but have the potential to impact drinking water, crops and other agricultural impacts

SYSTEMS THINKING

Compiled data from cast

Calculated biosolid use by county

Literature review of PFAS

Used R studio to create maps

PROFESSIONAL DEVELOPMENT

Made connections in the USGS and EPA offices, and got a lot of experience in a variety of settings, and learning what I might want from a career in the future

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SOURCES

Blake, B.E., and Fenton, S.E., 2020, Early life exposure to per- and polyfluoroalkyl substances (PFAS) and latent health outcomes: A review including the placenta as a target tissue and possible driver of peri- and postnatal effects: Toxicology, v. 443, p. 152565.

Buck, R.C., Franklin, J., Berger, U., Conder, J.M., Cousins, I.T., De Voogt, P., Jensen, A.A., Kannan, K., Mabury, S.A., and Van Leeuwen, S.P., 2011, Perfluoroalkyl and polyfluoroalkyl substances in the environment: Terminology, classification, and origins: Integrated Environmental Assessment and Management, v. 7, no. 4, p. 513–541.

Chesapeake Bay Program, 2020. Chesapeake Assessment and Scenario Tool (CAST) Version 2019. Chesapeake Bay Program Office, Last accessed [July, 2023].

do Carmo Precci Lopes, A., Ebner, C., Gerke, F., Wehner, M., Robra, S., Hupfauf, S., and Bockreis, A., 2022, Residual municipal solid waste as co-substrate at wastewater treatment plants: An assessment of methane yield, dewatering potential and microbial diversity: Science of The Total Environment, v. 804, p. 149936.

Environmental Protection Agency, 1994, A Plain English Guide to the EPA Part 503 Biosolids Rule.: p. 176.

Gravesen, C.R., Lee, L.S., Choi, Y.J., Silveira, M.L., and Judy, J.D., 2023, PFAS release from wastewater residuals as a function of composition and production practices: Environmental Pollution, v. 322, p. 121167.

ITRC, 2022, Environmental Fate and Transport Process, at ITRC at https://pfas-1.itrcweb.org/5-environmental-fate-and-transport-processes/#5_2.

Johnson, G.R., 2022, PFAS in soil and groundwater following historical land application of biosolids: Water Research, v. 211, p. 118035.

Kleinfelder, J.H., 2022, PFAS Chemistry and Naming Conventions, History and Use of PFAS, and Sources of PFAS Releases to the Environment, at ITRC at https://pfas-1.itrcweb.org/2-pfas-chemistry-and-naming-conventions-history-and-use-of-pfas-and-sources-of-pfas-releases-to-the-environment-overview/.

MABA, 2022, Per- and Polyfluorinated Substances (PFAS), accessed June 20, 2023, at https://maba.memberclicks.net/per--and-polyfluorinated-substances--pfas-.

Schultz, M.M., Higgins, C.P., Huset, C.A., Luthy, R.G., Barofsky, D.F., and Field, J.A., 2006, Fluorochemical Mass Flows in a Municipal Wastewater Treatment Facility: Environmental Science & Technology, v. 40, no. 23, p. 7350–7357.

Sepulvado, J.G., Blaine, A.C., Hundal, L.S., and Higgins, C.P., 2011, Occurrence and Fate of Perfluorochemicals in Soil Following the Land Application of Municipal Biosolids: Environmental Science & Technology, v. 45, no. 19, p. 8106–8112.

Venkatesan, A.K., and Halden, R.U., 2013, National inventory of perfluoroalkyl substances in archived U.S. biosolids from the 2001 EPA National Sewage Sludge Survey: Journal of Hazardous Materials, v. 252–253, p. 413–418.

Wang, Y., Chang, W., Wang, L., Zhang, Y., Zhang, Y., Wang, M., Wang, Y., and Li, P., 2019, A review of sources, multimedia distribution and health risks of novel fluorinated alternatives: Ecotoxicology and Environmental Safety, v. 182, p. 109402.

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THANK YOU

Emily Majcher

Andyrew Seckellick

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