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Published online 4 January 2008
Published in J Environ Qual 37:22-29 (2008)
DOI: 10.2134/jeq2007.0142
© 2008 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
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Ecological Effects after an Alum Treatment in Spring Lake, Michigan

Alan D. Steinman* and Mary Ogdahl

Annis Water Resources Inst., Grand Valley State Univ., 740 West Shoreline Drive, Muskegon, MI 49441


Figure 1
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Fig. 1. Site map of Spring Lake, showing location of four sampling sites. Inset: Outline of Michigan's lower peninsula, with encircled dot showing location of Spring Lake.

 

Figure 2
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Fig. 2. Selected limnological characteristics (temperature, dissolved oxygen, and chlorophyll a) at Sites 1 through 4 in July 2006 post-alum treatment.

 

Figure 3
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Fig. 3. Mean + 1 SE invertebrate densities (organisms m–2) of major groups in Spring Lake in 2004 and 2006.

 

Figure 4
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Fig. 4. Total invertebrate density (mean + 1 SE) (organisms m–2) in Spring Lake in 2004 and 2006.

 

Figure 5
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Fig. 5. Total phosphorus (TP) concentrations measured in water column above sediment cores taken from Sites 1 through 4 exposed to two different redox conditions. Data are means ± 1 SD (n = 3).

 

Figure 6
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Fig. 6. Total phosphorus (TP) concentration in dry sediment (mg kg–1) from summer 2006 sediment cores analyzed before and at the end of the laboratory incubations.

 

Figure 7
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Fig. 7. (A) Soluble reactive phosphorus (SRP) concentrations in sediment porewater of cores at the end of the incubation period. (B) Sodium hydroxide– and HCl-extractable SRP concentrations in core sediment at the end of the incubation period.

 





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