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Phosphorus Loading Effects on Extracellular Enzyme Activity in Everglades Wetland Soils

A.L. Wright and K.R. Reddy

Wetland Biogeochemistry Lab., Univ. of Florida, 106 Newell Hall, P.O. Box 110510, Gainesville, FL 32611



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Fig. 1. Alkaline phosphatase activity (mg of p-nitrophenol g soil-1 h-1) in detritus and two soil depths along the P gradient in WCA-2A for four sampling times. Error bars represent standard error

 


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Fig. 2. Alkaline phosphatase activity in detritus and two soil depths along the P gradient in WCA-2A expressed as a percentage of maximum APA for each sampling time. Data for each depth represent an average of four sampling times. Error bars represent standard error

 


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Fig. 3. Alkaline phosphatase activity in detritus expressed as a percentage of maximum plotted against bicarbonate-extractable P (NaHCO3–Pi). Data represent an average of the February and August 1996 and March 1997 sampling times. Error bars represent standard error

 


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Fig. 4. Arylsulfatase activity (mg of p-nitrophenol g soil-1 h-1) in detritus and two soil depths at the February, May, and August 1996 sampling times in P-impacted, transitional, and unimpacted areas. Error bars represent standard error

 


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Fig. 5. ß-D-glucosidase (mg of p-nitrophenol g soil-1 h-1) activity in detritus and two soil depths at the February, May, and August 1996 sampling times in P-impacted, transitional, and unimpacted areas. Error bars represent standard error

 


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Fig. 6. Protease activity (mg of tyrosine g soil-1 h-1) in detritus and two soil depths at the May and August 1996 sampling times in P-impacted, transitional, and unimpacted areas. Error bars represent standard error

 


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Fig. 7. Phenol oxidase activity (µmol diqc g-1 min-1) in detritus and two soil depths at the May and August 1996 sampling times in P-impacted, transitional, and unimpacted areas. Error bars represent standard error

 





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