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Abstract Humid tropical forests are among the most productive ecosystems globally, yet they often occur on soils with high phosphorus (P) sorption capacity, lowering P availability to biota. Short‐term anoxic events are thought to release sorbed P and enhance its acquisition by soil microbes. However, the actual effects of anoxic conditions on microbial P acquisition in humid tropical forest soils are surprisingly poorly studied. We used laboratory incubations of bulk soils, NanoSIMS analysis of single microbial cells, and landscape‐scale measurements in the Luquillo Experimental Forest (LEF), Puerto Rico to test the hypothesis that anoxic conditions increase microbial P acquisition in humid tropical forests. In laboratory and field experiments, we found that microbial P uptake generally decreased under anoxic conditions, leading to high microbial carbon (C) to P ratios in anoxic soils. The decreased P acquisition under anoxic conditions was correlated with lower microbial C use efficiency (CUE), an index of microbial energy transfer in ecosystems. Phosphorus amendments to anoxic soils led to increased microbial P uptake and higher CUE suggesting that microbes were less able to access and utilize P under natural low redox conditions. Under oxic conditions, microbial C:P ratios and CUE did not respond to changes in substrate stoichiometry. These results challenge the existing paradigm by showing that anoxic conditions can decrease microbial P uptake and ultimately constrain microbial CUE. Our findings indicate that soil redox conditions tightly couple soil P and C cycles and advance our understanding of controls on P cycling in humid tropical forest ecosystems.
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Anoxic conditions maintained high phosphorus sorption in humid tropical forest soils
Abstract. The strong phosphorus (P) sorption capacity of iron (Fe)and aluminum (Al) minerals in highly weathered, acidic soils of humidtropical forests is generally assumed to be an important driver of Plimitation to plants and microbial activity in these ecosystems. Humidtropical forest soils often experience fluctuating redox conditions thatreduce Fe and raise pH. It is commonly thought that Fe reduction generallydecreases the capacity and strength of P sorption. Here we examined theeffects of 14 d oxic and anoxic incubations on soil P sorption dynamics inhumid tropical forest soils from Puerto Rico. Contrary to the conventionalbelief, soil P sorption capacity did not decrease under anoxic conditions,suggesting that soil minerals remain strong P sinks even under reducingconditions. Sorption of P occurred very rapidly in these soils, with atleast 60 % of the added P disappearing from the solution within 6 h.Estimated P sorption capacities were much higher, often by an order ofmagnitude, than the soil total P contents. However, the strength of Psorption under reducing conditions was weaker, as indicated by the increasedsolubility of sorbed P in NaHCO3 solution. Our results show that highlyweathered soil minerals can retain P even under anoxic conditions, where itmight otherwise be susceptible to leaching. Anoxic events can alsopotentially increase P bioavailability by decreasing the strength, ratherthan the capacity, of P sorption. These results improve our understanding ofthe redox effects on biogeochemical cycling in tropical forests.
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- Award ID(s):
- 1831952
- PAR ID:
- 10207109
- Date Published:
- Journal Name:
- Biogeosciences
- Volume:
- 17
- Issue:
- 1
- ISSN:
- 1726-4189
- Page Range / eLocation ID:
- 89 to 101
- Format(s):
- Medium: X
- Sponsoring Org:
- National Science Foundation
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interactions between phosphate and various Fe (oxyhydr)oxides are poorly constrained in natural systems. An in-situ incubation experiment was conducted to explore Fe (oxyhydr)oxide transformation and effects on phosphate sorption in soils with contrasting saturation and redox conditions. Synthetic Fe (oxyhydr)oxides (ferrihydrite, goethite and hematite) were coated onto quartz sand and either pre-sorbed with phosphate or left phosphate-free. The oxide-coated sands were mixed with natural organic matter, enclosed in mesh bags, and buried in and around a vernal pond for up to 12 weeks. Redox conditions were stable and oxic in the upland soils surrounding the vernal pond but largely shifted from Fe reducing to Fe oxidizing in the lowland soils within the vernal pond as it dried during the summer. Iron (oxyhydr)oxides lost more Fe (− 41% ± 10%) and P (− 43 ± 11%) when incubated in the redox-dynamic lowlands compared to the uplands (− 18% ± 5% Fe and − 24 ± 8% P). Averaged across both uplands and lowlands, Fe losses from crystalline goethite and hematite (− 38% ± 6%) were unexpectedly higher than losses from short range ordered ferrihydrite (− 12% ± 10%). We attribute losses of Fe and associated P from goethite and hematite to colloid detachment and dispersion but losses from ferrihydrite to reductive dissolution. Iron losses were partially offset by retention of solubilized Fe as organic-bound Fe(III). Iron (oxyhydr)oxides that persisted during the incubation retained or even gained P, indicating low amounts of phosphate sorption from solution. These results demonstrate that hydrologic variability and Fe (oxyhydr)oxide mineralogy impact Fe mobilization pathways that may regulate phosphate bioavailability.more » « less
- Free Publicly Accessible Full Text
-
Accepted Manuscript1.0
- Journal Article:
- https://doi.org/10.5194/bg-17-89-2020
