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  • Hart, Stephen C.  (4)
  • Geography  (4)
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  • Geography  (4)
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  • 1
    Online Resource
    Online Resource
    Wiley ; 2023
    In:  Journal of Plant Nutrition and Soil Science Vol. 186, No. 1 ( 2023-02), p. 116-129
    In: Journal of Plant Nutrition and Soil Science, Wiley, Vol. 186, No. 1 ( 2023-02), p. 116-129
    Abstract: Nitrogen (N) is an essential nutrient in soil that regulates plant growth, terrestrial sequestration of atmospheric carbon dioxide, and persistence of organic compounds. However, major knowledge gaps remain about how climate change may impact N accumulation and persistence, especially in deep soil and saprock (friable weakly weathered bedrock). Aims Our objective was to understand how climate impacts the accumulation of N in soil and saprock and how climate impacts soil N distribution, persistence, and mechanisms of N persistence. Methods We investigated N concentration in bulk soil and density fractions. We estimated N persistence along a bio‐climatic sequence—sites range from a low‐elevation oak savannah, mid‐elevation pine‐oak/mixed‐conifer forest, to a high‐elevation subalpine forest—in the southern Sierra Nevada in California. A combination of radiocarbon and elemental composition measurements along with a first‐order kinetic model was used. Results The N concentration in the bulk soil and density fractions declined with depth, and there was a relatively greater mineral‐associated heavy fraction (HF) N in deeper samples. The cooler/wetter mixed conifer site held 37% of profile N in saprock, which was greater than that of the entire soil profile at the drier/hotter oak savannah. The majority of N in soil, which was in the HF, was not influenced by climate proxies tested. However, both unprotected and occluded fractions of N were strongly influenced by climate. Soil N mean residence time (MRT) showed that drier/hotter climates have a shorter MRT, compared to mid‐elevation sites with cooler/wetter climates. Conclusions The effect of climate on deep saprock N storage might be indirect, primarily through climatic influence on the thickness of saprock. Overall, our findings suggest the mineral‐associated HF N pool will not be vulnerable to changes in climate and will continue to contribute to the persistent soil N pool. The amount of topsoil and subsoil unprotected and occluded N can be explained by gross primary productivity and mean annual precipitation indicating that changes in climate can influence N partitioning. N stored in deep soil and saprock may be less vulnerable to climate than N stored in drier/hotter climates with less deeply stored N. It is critical to dig deeper to understand terrestrial ecosystems’ response to climate.
    Type of Medium: Online Resource
    ISSN: 1436-8730 , 1522-2624
    URL: Issue
    RVK:
    Language: English
    Publisher: Wiley
    Publication Date: 2023
    detail.hit.zdb_id: 1481142-X
    detail.hit.zdb_id: 1470765-2
    SSG: 12
    SSG: 13
    Location Call Number Limitation Availability
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  • 2
    Online Resource
    Online Resource
    Wiley ; 1998
    In:  Soil Science Society of America Journal Vol. 62, No. 4 ( 1998-07), p. 1062-1072
    In: Soil Science Society of America Journal, Wiley, Vol. 62, No. 4 ( 1998-07), p. 1062-1072
    Abstract: In ponderosa pine ( Pinus ponderosa Douglas ex P. Lawson & Lawson)‐bunchgrass ecosystems of the western USA, fire exclusion by Euro‐American settlers facilitated pine invasion of grassy openings, increased forest floor detritus, and shifted the disturbance regime toward stand‐replacing fires, motivating ecological restoration through thinning and prescribed burning. We used in situ soil respiration over a 2‐yr period to assess belowground responses to pine invasion and restoration in a ponderosa pine‐bunchgrass ecosystem near Flagstaff, AZ. Replicated restoration treatments were: (i) partial restoration — thinning to presettlement conditions; (ii) complete restoration — removing trees and forest floor material to presettlement conditions, native grass litter addition, and prescribed burning; and (iii) control. Within treatments, we sampled beneath different canopy types to assess the effects of pine invasion into grassy openings on soil respiration. Growing season soil respiration was greater in the complete restoration (346 ± 24 g CO 2 ‐C m ‐2 ) and control (350 ± 8 g CO 2 ‐C m ‐2 ) than the partial restoration (301 ± 5 g CO 2 ‐C m ‐2 ) in 1995. In 1996, the complete (364 ± 17 g CO 2 ‐C m ‐2 ) and partial (328 ± 7 g CO 2 ‐C m ‐2 ) restoration treatments had greater growing season respiration rates than the control (302 ± 13 g CO 2 ‐C m ‐2 ). Results suggest that restoration effects on soil respiration depend on interannual soil water patterns and may not significantly alter regional C cycles. Soil respiration from grassy openings was 15% greater than from soil beneath presettlement or postsettlement pines in 1995 and 1996. A lack of active management will decrease belowground catabolism if pines continue to expand at the expense of grassy openings.
    Type of Medium: Online Resource
    ISSN: 0361-5995 , 1435-0661
    RVK:
    Language: English
    Publisher: Wiley
    Publication Date: 1998
    detail.hit.zdb_id: 196788-5
    detail.hit.zdb_id: 1481691-X
    SSG: 13
    SSG: 21
    Location Call Number Limitation Availability
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  • 3
    Online Resource
    Online Resource
    Wiley ; 2005
    In:  Soil Science Society of America Journal Vol. 69, No. 5 ( 2005-09), p. 1627-1638
    In: Soil Science Society of America Journal, Wiley, Vol. 69, No. 5 ( 2005-09), p. 1627-1638
    Abstract: In ponderosa pine ( Pinus ponderosa Dougl. ex Laws.) forests of the western USA, fire exclusion by Euro‐American settlers facilitated pine invasion of grass openings, increased forest floor detritus, and shifted the disturbance regime toward stand‐replacing fires. We evaluated the impacts of two replicated ecological restoration treatments involving tree thinning alone (thinning restoration) and a combination of tree thinning, forest floor reduction, and prescribed burning (composite restoration) on soil microbial activity, biomass, and function approximately 8 yr after initial treatments. Microbial‐N levels in the two restoration treatments were not significantly different from the control during either the dry or wet periods of the growing season. Soil respiration measured in situ was significantly higher in the restoration treatments than in the control only during the dry period, while soil enzyme activities were generally higher in the composite restoration treatment than in the thinning restoration or control treatments during the wet period. Community‐level physiological profiles suggested differences in the physiological capacities of bacteria and fungi in the composite restoration treatment compared with the other treatments. We also compared microbial characteristics under different canopy types to evaluate the impacts of pine invasion and establishment in grass openings on soil microorganisms. Soil respiration rates (dry period only) and enzyme activities (wet period only) were higher in grass openings than under presettlement trees, with intermediate values found under postsettlement pines that have invaded grass areas. Taken together, our results suggest that restoration treatments have long‐term impacts on the soil microflora in these forests.
    Type of Medium: Online Resource
    ISSN: 0361-5995 , 1435-0661
    RVK:
    Language: English
    Publisher: Wiley
    Publication Date: 2005
    detail.hit.zdb_id: 196788-5
    detail.hit.zdb_id: 1481691-X
    SSG: 13
    SSG: 21
    Location Call Number Limitation Availability
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  • 4
    Online Resource
    Online Resource
    Wiley ; 1996
    In:  Soil Science Society of America Journal Vol. 60, No. 6 ( 1996-11), p. 1846-1855
    In: Soil Science Society of America Journal, Wiley, Vol. 60, No. 6 ( 1996-11), p. 1846-1855
    Abstract: When diffusion techniques are used to prepare samples for 15 N analyses, low or variable N recovery is sometimes observed. The effect of low recovery on estimates of 15 N enrichment is unknown. Also, the suitability of diffusion techniques for use with a variety of salt solutions and digests containing very low N concentrations ( 〈 0.8 mg L −1 ) has not been determined. We evaluated a diffusion technique where NH 3 ‐N is trapped on acidified filter paper disks that are sealed between two strips of Teflon [polytetrafluoroethylene (PTFE)] tape. Because the PTFE protects the acid trap from neutralization, large volumes of solution can be diffused in plastic specimen containers and the sample can be vigorously mixed during the diffusion period. Six days of diffusion at 22°C resulted in 〉 92% recovery of 50 µg NH + 4 ‐N from 75 mL of 2 M NaCl, total Kjeldahl digests, or 2 M KCl preserved with acid. Leaving sample containers open for 5 d after diffusion for NH + 4 completely eliminated contamination of NO − 3 ‐N by residual NH + 4 ; however, recovery of NO − 3 was inversely related to the length of the open period. Recovery of NO 3 − ‐N from 0.5 M K 2 SO 4 and alkaline persulfate digests after a 3‐d open period was 90 and 77%, respectively. Complete recovery of NH + 4 or NO − 3 was not required to obtain accurate estimates of 15 N enrichment; however, when recovery was 〈 100%, the method of blank correction was critical. When the mass of N contamination measured in diffusion blanks was used to blank‐correct 15 N enrichments, diffused standards often had 15 N enrichments that were significantly different from nondiffused standards; however, when the mass of N in blanks was estimated using an isotope dilution equation, there was excellent agreement between diffused and nondiffused standards, regardless of the degree of recovery.
    Type of Medium: Online Resource
    ISSN: 0361-5995 , 1435-0661
    RVK:
    Language: English
    Publisher: Wiley
    Publication Date: 1996
    detail.hit.zdb_id: 196788-5
    detail.hit.zdb_id: 1481691-X
    SSG: 13
    SSG: 21
    Location Call Number Limitation Availability
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