Acid sulfate soils in dredged materials from tidal Pocomoke Sound in Somerset County, MD, USA
S. Y. Demas A C , A. M. Hall A , D. S. Fanning B , M. C. Rabenhorst B and E. K. Dzantor BA U.S. Department of Agriculture, Natural Resources Conservation Service, 30730 Park Drive, Princess Anne, MD 21853-1035, USA.
B Department of Natural Resources Sciences and Landscape Architecture, University of Maryland, College Park, MD 20742-4452, USA.
C Corresponding author; email: susan.demas@md.usda.gov
Australian Journal of Soil Research 42(6) 537-545 https://doi.org/10.1071/SR03089
Submitted: 11 July 2003 Accepted: 16 February 2004 Published: 17 September 2004
Abstract
Seepage and runoff waters from soils forming in sulfide-bearing dredge materials (SBDM) can have dramatic effects on water quality if they are placed adjacent to open water and do not have adequate containment. Soils forming in SBDM can produce large amounts of acidity upon sulfide oxidation and the oxidation and hydrolysis of released ferrous iron when they are drained or otherwise exposed to air. These soils, under certain environmental conditions, can produce low pH seepage and runoff waters containing large amounts of iron and aluminum, especially after heavy rain that follows a prolonged dry period. During the course of the soil survey update of Somerset County, Maryland (MD), USA, 2 areas of soils forming in SBDM of differing age were identified in close proximity to the sites of recent fish kills on the Pocomoke Sound in Somerset County. Both of these soil areas were initially contained by earthen berms. The dredge materials were deposited directly over the natural tidal marsh soil. Soils forming in SBDM that are approximately 60 years of age were classified as fine-silty, mixed mesic Sulfic Endoaquepts, while the second area of SBDM are 8 years of age and classified as fine-silty, mixed, mesic Typic Sulfaquepts, by Soil Taxonomy. The presence of jarosite was confirmed in both soils by X-ray diffraction, and the presence of ironstone (iron oxyhydroxides) was confirmed in both soils at the effluent discharge points. This is an indication that these soils have undergone intensive acid sulfate weathering (sulfuricization) and that they have released a large quantity of iron to waters leaving the sites. Studies have shown that the 2 mechanisms responsible for acid production from soils forming in SBDM are (i) the oxidation and hydrolysis of mobile ferrous iron; and (ii) the oxidation of the sulfur occurring in the form of pyrite. It is suggested that the resultant low pH, Fe- and Al-enriched water from these soils that entered the Pocomoke Sound may have made fish more susceptible to microbial predation by weakening mucous membranes and/or by promoting the growth of harmful cyannobacteria and flagellates. This paper reports the nature and classification of soils that developed in SBDM at 2 sites of differing age and of the possible environmental impacts of seepage and runoff from these sites entering the Pocomoke Sound.
Additional keywords: sulfide, sulfuricization, acid sulfate, fish kills, iron, aluminum.
† Low dissolved oxygen levels were additionaly recorded doring the 22 July 1999 event.
Acknowledgment
We wish to express our gratitude to Bill McInturff, State of Maryland, Department of Natural Resources, for his help in securing site access as well as providing site history information.
Bohn, HL ,
McNeal, BL ,
and
O'Conner, GA (1979).
Brown TE,
Morley AW,
Sanderson NT, Tait RD
(1983) Report of a large fish kill resulting from natural acid water conditions in Australia. Journal of Fish Biology 22, 335–350.
Callinan RB, Frazer GC, Melville MD
(1993) Seasonally recurrent fish mortalities and ulcerative disease outbreaks associated with acid sulphate soils in Australian estuaries. ‘Selected Papers of the Ho Chi Minh City Symposium on Acid Sulphate Soils’. International Institute for Land Reclamation and Improvement Publication No. 53.. (Ed. DL Dent ,
MEF van Mensvoort )
pp. 403–410. (International Institute for Land Reclamation and Improvement: Wageningen, The Netherlands)
Clesceri, S ,
Eaton, AD ,
and
Greenberg, AE (1998).
Cornwell JC, Morse JW
(1987) The characterization of sulfide minerals in anoxic sediments. Marine Chemistry 22, 193–206.
| Crossref | GoogleScholarGoogle Scholar |
Day, JW ,
Hall, CAS ,
Kemp, WM ,
and
Yáñez-Arancibia, A (1989).
Dennison WC,
O'Niel JM,
Duffy EJ,
Oliver PE, Shaw GR
(1999) Blooms of the cyanobacterium Lyngbya majuscula majuscula in coastal waters of Queensland, Australia. Bulletin de l'Institut oceanographique 19, 501–506.
Dent DL, Raiswell RW
(1982) Quantitative models to predict the rate and severity of acid sulphate development: A case study in the Gambia. ‘Proceedings of the Bangkok Symposium on Acid Sulfate Soils’. International Institute for Land Reclamation and Improvement Publication No. 31. (Ed. H Dost ,
N van Breeman )
pp. 73–95. (International Institute for Land Reclamation and Improvement: Wageningen, The Netherlands)
Fanning DS, Burch SN
(1997) Acid sulfate soils and some associated environmental problems. ‘Soils and environment’. Advances in Geoecology No. 30. (Ed. K Auerswald ,
H Stanjek ,
JM Bigham )
pp. 145–158. (Catena Verlag: Reiskirchen, Germany)
Fanning DS, Burch SN
(2000) Coastal acid sulfate soils. ‘Reclamation of drastically disturbed lands’. Agronomy Monograph No. 41. (Ed. RI Barnhisel ,
RG Darmody ,
WL Daniels )
pp. 921–937. (American Society of Agronomy: Madison, WI)
Fanning, DS ,
and
Fanning, MCB (1989).
Fanning DS, Rabenhorst MC, Burch SN, Islam KR, Tangren SA
(2002) Sulfides and sulfates. ‘Soil mineralogy with environmental applications’. Book Series No. 7.. (Ed. JB Dixon ,
DG Schulze ,
WL Daniels )
pp. 229–260. (Soil Science Society of America: Madison, WI)
Gee GW, Bauder JW
(1986) Particle-size analysis. ‘Methods of soil analysis. Part 1. Physical and mineralogical methods’. (Ed. A Klute)
pp. 383–411. (American Society of Agronomy: Madison, WI)
Griffin TM,
Rabenhorst MC, Fanning DS
(1989) Iron and trace metals in some tidal marsh soils of the Chesapeake Bay. Soil Science Society of America Journal 53, 1010–1019.
Hoeft RG,
Walsh LM, Keeny DR
(1973) Evaluation of various extractants for available soil sulfur. Soil Science Society of America Proceedings 37, 401–404.
Matthews, ED ,
and
Hall, RL (1966).
Sammut J, Callahan RB, Dove M
(1999) A brief review of the aquatic impacts of acid sulfate soils. ‘Acid Sulfate Soils and their Management in Coastal Queensland—Forum and Technical Papers’. Section 4. : Brisbane, Qld)
Sammut, J ,
and
Lines-Kelly, R (2000).
Sammut J,
White I, Melville MD
(1996) Acidification of an estuarine tributary in eastern Australia due to drainage of acid sulfate soils. Marine and Freshwater Research 47, 669–684.
Schulte EE, Elk K
(1988) Recommended sulfate-S test. Recommended chemical soil test procedures for the North Central Region North Dakota Agricultural Experiment Station Bulletin 499,(Ed. WC Danke)
pp. 17–20. )
Shoeneberger, PJ ,
Wysocki, DA ,
Benham, EC ,
and
Broderson, WD (2002).
Soil Survey Staff
(1993)
Soil Survey Staff
(1999)
Sullivan LA, Bush RT, Fyfe D
(2002) Acid sulfate soil drain ooze: Distribution, behavior and implications for acidification and deoxygenation of waterways. ‘Acid sulfate soils in Australia and China’. (Eds C Lin, MD Melville, LA Sullivan)
pp. 91–99. (Science Press: Beijing)