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- Materials and Methods
Understanding the dynamics of nutrient-limited grasslands and savannas and informing ecosystem stewards as to best management practices for these ecosystems first require determination of which nutrients are limiting primary production. Nutrient addition experiments are the classic approach to determining which nutrients limit primary production and the relative degrees of limitation at a given site (Chapin et al., 1986; Vitousek & Howarth, 1991). In grasslands, many different nutrients can limit production and often different nutrients co-limit productivity (e.g. Olff & Pegtel, 1994). Yet, fertilization studies can be intensive undertakings and their results can be difficult to interpret when vegetation does not respond to a given nutrient (Rastetter & Shaver, 1992; Aerts & Chapin, 2000). As such, nitrogen (N) and phosphorus (P) ratios in vegetation have been offered as a simpler index of the limitation of N and P (Penning de Vries et al., 1980; Koerselman & Meuleman, 1996; Tessier & Raynal, 2003; Güsewell, 2004) and have been used to describe broad geographic patterns of nutrient limitation (Reich & Oleksyn, 2004; Wassen et al., 2005).
The use of N:P ratios as an index of nutrient limitation appears to be well rooted in ecological theory and has strong support in the literature. Empirically, N:P ratios have been shown to be effective predictors of nutrient limitation. Most notably, in a review of 40 wetland fertilization studies from northern Europe, vegetation N:P predicted the response of aboveground net primary production to fertilizations (Koerselman & Meuleman, 1996). When plant N:P, expressed as a ratio of mass concentrations, was < 14, N was limiting. When plant N:P was > 16, P was limiting. In between, N and P were co-limiting. Tessier & Raynal (2003) recently reviewed fertilization studies in upland ecosystems and they supported the use of ratios to predict limitation, stating that ‘N:P ratios can be effective predictors of nutrient limitation in upland ecosystems [and] can be used for management and monitoring purposes in considering the nutrient status of upland ecosystems’. Güsewell (2004) proposed a broader range of ratios for co-limitation of plant communities, stating that ‘it appears that biomass production is most likely to be enhanced by N fertilization in vegetation with N:P ratio < 10 and by P fertilization in vegetation with N:P ratio > 20, whereas within this range, the effects of fertilization are not unequivocally related to N:P ratios.’
Despite the apparent support for its utility across two recent reviews (Tessier & Raynal, 2003; Güsewell, 2004), the ability of plant N:P to generally predict whether N and/or P is limiting in grasslands should be revisited. First, Tessier & Raynal (2003) largely rely on changes in nutrient concentrations as an index of nutrient limitation, as opposed to increases in biomass or production. Yet, increases in nutrient concentrations with fertilization do not necessarily precede increases in production and their conclusions would not necessarily apply to limitation of production. Secondly, Güsewell (2004) relied on two publications in assessing critical N:P ratios for limitation in upland vegetation. The first was Tessier & Raynal (2003), which suffers from relying on responses of concentrations, not biomass, to fertilization. The second was Penning de Vries et al. (1980), which discussed nutrient limitation in Sahelian grasslands. In the paper, the authors suggest critical N:P ratios of 6.6 and 27, but the evidence for these was drawn from unpublished studies and relied on changes in nutrient concentrations, not increases in biomass. Although these suggestions of critical N:P ratios might be suitable for hypothesis generation, they cannot be considered evidence for specific critical ratios of limitation.
To better understand the patterns of N and P limitation in grasslands, and to test whether ratio thresholds are appropriate for these ecosystems, we test the ability of N:P to predict limitation across five sites in Kruger National Park (KNP), South Africa and then compare those results with those of recently published grassland fertilization studies. At KNP, we fertilized a range of sites that differed in soil parent material (either basalt or granite) and mean annual precipitation. Basalt soils are relatively rich in base cations compared with the granite soils (Venter et al., 2003), but foliar N:P is relatively low for both soil types. Across landscape positions and seasons, Grant & Scholes (2006) found that mean foliar N:P ratios were 6.9 on basalts and 10.5 on granites, with N:P as low as 3 on both soil types. If N:P ratios index nutrient limitation in these ecosystems, we expected that aboveground biomass should primarily respond to N addition. Independent of any specific threshold, vegetation on granite soils, which has higher N:P, should respond more to P addition or be more likely to respond to P alone than that on basalt sites. To test these predictions, we compare average responses of aboveground biomass to fertilization for all five sites, variation in responses across the sites, and the responses of plots fertilized with a single nutrient with those of plots fertilized with both N and P.
Materials and Methods
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- Materials and Methods
Five sites were selected for experimental N and P additions in KNP, which covers approx. 2 × 106 ha in northeastern South Africa, and is largely savanna and grassland with soils generally derived from basalt parent material in the eastern portion of the park and from granites in the west. Precipitation is highest in the southwest and declines eastward and northward. Fire is an important component of most KNP ecosystems, and a diverse contingent of herbivores are present, including megaherbivores. Two sites were selected on granite soils (Pretoriuskop and Letaba) and the other three sites were on basalt soils (Makhohlola, Satara, and Nwashitsumbe) (Table 1). Data for each site on soil texture, water holding capacity, pH, carbon (C) and N concentrations, Bray II available P, and 56-d potential N mineralization were taken from Craine et al. (2007).
Table 1. Site characteristics for the five sites used in this study
|Collection date||27 Mar 04||19 Mar 05||26 Mar 04||1 Apr 05||30 Mar 05|
|Soil C (mg g−1)||3.3||4.76||21.92||18.64||16.76|
|Soil N (mg g−1)||0.52||0.76||1.42||1.59||1.67|
|P Bray II (mg kg−1)||3.23||11.32||85.43||53.17||39.45|
|Nmin (µmol g−1)||0.63||0.10||2.10||0.43||0.99|
Each site contained 32 2 m × 2 m plots with treatments randomized among plots. Fertilizer was applied in July 2003 and March 2004. Eight plots received no fertilizer, eight received additional N in the form of NH4NO3 at a rate of 10 g m−2 yr−1, eight received additional P in the form of superphosphate (91.6 mg g−1 P, 250 mg g−1 calcium (Ca) and 132 mg g−1 sulphur (S)) at a rate of 5 g P m−2 yr−1, and eight received additional N and P at the same rates as the single-nutrient addition plots. All vegetation was trimmed to 5 cm at the initiation of the experiment in June 2003 and again after the March 2004 harvest in order to mimic the removal of biomass that generally occurs regularly via fire or grazing in KNP.
In January and March of 2004 and 2005, 0.1 m2 of biomass was clipped from each plot at a height of 5 cm. Biomass was separated into grass and dicotyledonous biomass, dried at 40°C and then weighed. Very little dead biomass was observed in any of the samples and forb biomass was an average of only 11% of total biomass. Grass biomass for each harvest except March 2004 was then ground and analyzed for C, N, and P concentrations. C and N concentrations were determined via combustion on an elemental analyzer (Carlo-Erba, Milan, Italy). For P concentrations, leaf biomass was first digested in a 10 : 1 : 1 mixture of HNO3, HClO4, and H2SO4 for 60 min at 150°C followed by 20 min at 250°C. Phosphorous concentrations were determined on distilled water extract of the residuum with malachite green colorimetry (Diatloff & Rengel, 2001) on a Biotek Powerwave XS microplate spectrophotometer (Biotek Instruments, Inc., Winooski, VT, USA).
Fine root productivity was assessed during the 2005 growing season with ingrowth cores (Craine et al., 2002). At each plot during the March 2004 harvest, a 5-cm core to 25 cm depth was removed. Wire mesh was inserted into the hole to delineate the outside edge of the ingrowth core. The hole was refilled with sieved soil from the original core and the soil was tamped down by hand to approximate the bulk density of surrounding soil. Cores were harvested a year later during the March 2005 harvest by taking a 4-cm core from inside the mesh. Roots were washed, dried at 40°C and then weighed.
Data on biomass and nutrient concentrations over the four harvests were analyzed with a repeated measures ANOVA in jmp 5.0.1 (SAS Institute, Cary, NC, USA). As we discuss in the results, we compared fertilization responses within sites with additional ANOVAs, one for each site. We also ran individual ANOVAs for each harvest for illustrative purposes associated with graphical representation of differences among harvests in treatments, but consider these results less robust than the repeated measures ANOVA.
In adding two nutrients in factorial, there are two types of responses that would indicate co-limitation. First, biomass could increase when N is added individually as well as when P is added individually. Secondly, biomass could increase only when N and P are added together. If biomass increases significantly when one nutrient is added as well as when both nutrients are added, we consider vegetation to be co-limited when the increase in biomass from adding both nutrients relative to just one nutrient is greater than the increase in biomass from just adding one nutrient.
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- Materials and Methods
Average aboveground production for unfertilized plots was highest at the two high-precipitation sites, Pretoriuskop and Makhohlola (362 and 321 g m−2, respectively; Table 2), and lowest at the low-precipitation sites, Letaba and Nwashitsumbe (106 and 249 g m−2; Table 2). Production was greatest in March 2004, with January 2004 having the lowest biomass (586 g m−2 vs 118 g m−2; Fig. 1), although differences in production among sites varied over time (P < 0.001; Table 3, Fig. 1).
Table 2. Treatment differences among sites averaged among harvestsa
|Siteb||Treatment||[C]c,d||[N]||[P]||N:P||AG biomasse||2005 BNPP|
|Pretoriuskop||Control||424.3 ± 2.3b||7.8 ± 0.7b||0.9 ± 0.1c||9.2 ± 0.6b||362.4 ± 63.9b||267.3 ± 35.2a|
|N||436.6 ± 1.9a||9.1 ± 1.1a||0.6 ± 0.1c||17.7 ± 1.0a||455.9 ± 70.0ab||287.5 ± 68.4a|
|P||425.9 ± 2.5b||7.4 ± 0.9b||2.1 ± 0.1a||3.8 ± 0.5d||353.1 ± 62.6b||326.4 ± 90.3a|
|NP||427.4 ± 2.7b||10.7 ± 1.5a||1.5 ± 0.1b||7.1 ± 0.8c||488.7 ± 64.7a||278.2 ± 48.8a|
|Letaba||Control||411.7 ± 2.0a||9.6 ± 0.5c||1.5 ± 0.1a||6.6 ± 0.3c||105.9 ± 17.5c||231.6 ± 27a|
|N||410.7 ± 3.3a||15.6 ± 0.7a||1.4 ± 0.1a||11.5 ± 0.4a||134.0 ± 25.3bc||219.1 ± 25.4a|
|P||405.9 ± 4.6b||10.3 ± 0.5c||1.7 ± 0.1a||6.2 ± 0.3c||168.6 ± 28.3ab||326.4 ± 36.6a|
|NP||416.4 ± 2.4a||14.1 ± 0.8b||1.7 ± 0.1a||8.7 ± 0.4b||227.4 ± 61.4a||272.0 ± 95.6a|
|Makhohlola||Control||408.5 ± 3.5ab||9.1 ± 0.8b||2.8 ± 0.1a||3.2 ± 0.2b||321.2 ± 43.7b||208.3 ± 32.8a|
|N||416.2 ± 2.7a||13.0 ± 1.4a||2.3 ± 0.1b||5.8 ± 0.6a||368.2 ± 57.5b||231.6 ± 73.1a|
|P||404.4 ± 3.2b||10.1 ± 1.0b||2.6 ± 0.2a||3.9 ± 0.4b||322.9 ± 51.2b||206.7 ± 50.1a|
|NP||410.7 ± 2.5ab||13.8 ± 1.4a||2.2 ± 0.1b||6.2 ± 0.6a||514.0 ± 68.8a||223.8 ± 54.8a|
|Satara||Control||419.4 ± 2.5a||6.9 ± 0.4c||1.8 ± 0.1ab||4.4 ± 0.6b||294.2 ± 62.1b||296.9 ± 74a|
|N||419.5 ± 2.9a||11.0 ± 0.7a||1.7 ± 0.1ab||7.0 ± 0.6a||352.7 ± 56.2ab||225.6 ± 49.4a|
|P||418.9 ± 3.5a||8.7 ± 0.7bc||2.0 ± 0.2a||5.0 ± 0.7b||295.2 ± 48.8ab||303.1 ± 55.5a|
|NP||419.3 ± 7.4a||10.1 ± 1.0ab||1.4 ± 0.1b||7.0 ± 0.4a||532.6 ± 115.6a||267.3 ± 32.8a|
|Nwashitsumbe||Control||398.4 ± 2.5b||9.9 ± 0.6b||2.3 ± 0.2ab||5.1 ± 0.6c||247.8 ± 70.5a||110.4 ± 18.4a|
|N||398.4 ± 2.5b||14.1 ± 1.2a||2.1 ± 0.2b||7.5 ± 0.7b||253.2 ± 72.5a||144.5 ± 15.0a|
|P||397.7 ± 3.8b||9.6 ± 1.0b||2.5 ± 0.3a||4.5 ± 0.5c||157.7 ± 38.5a||138.3 ± 20.4a|
|NP||410.5 ± 2.9a||13.3 ± 1.1a||1.6 ± 0.1c||8.8 ± 0.8a||289.7 ± 89.2a||122.8 ± 13.8a|
|All sites||Control||412.4 ± 1.4ab||8.7 ± 0.3b||1.8 ± 0.1b||5.8 ± 0.3c||266.3 ± 25.3a||222.9 ± 37.5a|
|N||416.3 ± 1.7a||12.6 ± 0.5a||1.6 ± 0.1bc||9.9 ± 0.5a||312.8 ± 27.4a||221.7 ± 46.3a|
|P||410.9 ± 1.8b||9.2 ± 0.4b||2.2 ± 0.1a||4.7 ± 0.2d||258.9 ± 21.8a||260.2 ± 50.6a|
|NP||416.9 ± 1.8a||12.5 ± 0.6a||1.7 ± 0.1c||7.6 ± 0.3b||410.5 ± 37.8b||232.8 ± 49.1a|
Figure 1. Aboveground biomass for each treatment at each of four harvests averaged across sites. Differences among treatments in log-transformed aboveground biomass were determined with an ANOVA for each harvest, which is a less robust analysis than the repeated measures ANOVA reported in Table 3.
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Table 3. Results of repeated measures analyses for log-transformed aboveground biomass (AGB) and nutrient concentrationsa,b,c
| ||Log AGB||[N]||[P]||N:P|
|Site|| 4||45.8||< 0.001|| 4||31.5||< 0.001||71.5||< 0.001||82.7||< 0.001|
|Treatment|| 3||9.4||< 0.001|| 3||65.7||< 0.001||20.7||< 0.001||162.6||< 0.001|
|Site × treatment ||12||1.0||0.25||12||1.8||0.04||8.2||< 0.001||36.3||< 0.001|
|Harvest|| 3||24.3||< 0.001|| 2||147.1||< 0.001||23.4||< 0.001||49.7||< 0.001|
|Site × harvest||12||22.3||< 0.001|| 8|| 51||< 0.001||15.6||< 0.001||46.7||< 0.001|
|Treatment × harvest|| 9||0.9||0.16|| 6||7.1||< 0.001||0.9||0.56||3.0||< 0.001|
|Site × treatment × harvest||36||2.9||0.20||24||1.7||0.02||1.5||0.10||4.1||< 0.001|
The responses of aboveground biomass to fertilization indicate co-limitation between N and P that is consistent across sites and over time (Fig. 1, Table 3). When averaged across sites and over the four harvests, the addition of N or P alone did not lead to significant increases in aboveground biomass, although plots fertilized with N tended to have higher biomass than unfertilized plots (22% greater aboveground biomass). Plots fertilized with N and P had 54% higher biomass than control plots and 31% higher biomass than N-addition plots (Table 2). The effect of fertilization on aboveground biomass did not vary significantly across sites (P = 0.25) or harvests (P > 0.16; Table 3). Total forb biomass was unresponsive to fertilizer treatment (P > 0.05 for all four harvests) and fertilization did not alter fine root productivity in 2004–2005 (Table 2).
Although N and P both limited production, the N:P ratios for unfertilized vegetation were far below established thresholds for co-limitation. For plots that were not fertilized, averaged across all sites and dates, [N] was 8.7 mg g−1 and [P] was 1.8 mg g−1, generating a mean N:P of 5.8 (Table 2).
Comparing the biomass of plots fertilized with two nutrients to that of plots fertilized with just one is the equivalent of examining the response of vegetation fertilized with one nutrient to the addition of a second nutrient. Comparing N-fertilized vegetation with vegetation fertilized with both N and P, N:P ratios of N-fertilized vegetation were still lower than would have been expected based on established ratios for P limitation. The addition of N alone increased foliar N concentrations by 45% on average across sites and dates (Table 2). N fertilization did not alter P concentrations, resulting in significant increases in shoot N:P with N fertilization relative to control plots, although they remained relatively low (9.9 vs 5.8, respectively with a range of 5.8–17.7 among sites for N-fertilized plots).
Among sites, there was no relationship between the N:P of N-fertilized vegetation and the difference in biomass between co-fertilized plots and N-fertilized plots, whether expressed as a relative response or in terms of absolute biomass response (P > 0.25). Fertilization with P did increase P availability to plants as [P] increased by 22% (2.2 vs 1.8 mg g−1; Table 2) and these concentrations were higher than those for plants fertilized with N and P (1.7 mg P g−1). There was no significant change in N concentrations with P addition, leading to a decrease in N:P with P addition (5.8–4.7; Table 2).
Although there was no significant interaction between nutrient treatments and sites (Table 3), the trends among sites in responses to fertilization can be conservatively examined. Examining the patterns of nutrient concentrations across sites, N concentrations were similar among controls of basalt and granites sites (Table 2). Averaged across the three harvests, N concentrations varied by 43%, with the basaltic Satara having the lowest (6.9 mg g−1) and the basaltic Nwashitsumbe having the highest concentration (9.9 mg g−1). P concentrations were consistently higher on basalts than granites (Table 2), with average P concentration varying by 311% across all sites (Table 2). With generally greater P concentrations and similar N concentrations on the basalt sites compared with granite sites, granite sites consistently had higher N:P (Table 2). Yet, there was no general relationship between the average N:P of control plots for each site and the fractional increase in production with N or with N and P, or the marginal fractional increase in production from adding N and P over just N (P > 0.34 for all contrasts). If anything, the site with the highest N:P (Pretoriuskop, 9.2), and therefore the site least likely to be limited by N based on nutrient concentration ratios, was the only site that had biomass responses to fertilization that most resembled classical N limitation.
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Factorial fertilization with N and P in KNP grasslands revealed broad co-limitation of aboveground production across strong soil and precipitation contrasts. Three lines of evidence from this experiment raise questions about the utility of using N:P ratios for predicting nutrient limitation. First, the N:P of unfertilized vegetation, whose production was co-limited by N and P, was well below the relatively high threshold for co-limitation established in northern European wetlands by Koerselman & Meuleman (1996) (N:P < 14) and even below the relaxed threshold suggested by Güsewell (N:P < 10). Secondly, examining the N:P of vegetation fertilized with N, neither sets of thresholds predicted that vegetation would still be limited by P. Thirdly, there was no relationship between site N:P and the degree of limitation by N and P.
Although the observed limitation patterns at KNP would benefit from independent verification, there are multiple reasons suggesting that they are not misleading. First, although N fertilization did not significantly increase production, had the trend for increased biomass been significant, the general response to nutrient treatments should still be considered co-limitation more than serial limitation. The increases in production from adding N and P relative to just N were much larger than the nonsignificant increase from just adding N. Secondly, although the P fertilizer used in this experiment also contained Ca and S, changes in P concentrations with different treatments more parsimoniously support co-limitation with P than with the other two elements. When P was added alone, there was no biomass response and P concentrations increased (Table 2). When P and N were added together, biomass was greater than that of N-fertilized vegetation, but P concentrations did not increase above control levels (Table 2). Had it been Ca or S that was causing the increase in biomass with N, P, which is actively acquired by plants, would have continued to have been supplied in excess and accumulated in tissues just as occurred in P-fertilized plots. Lastly, as there was no difference in belowground production in 2005, the differences in aboveground productivity probably reflect Net Primary Productivity (NPP) and do not appear to be explained by a shift in production from belowground to aboveground.
The inability of N:P ratios to explain fertilization responses to N and P addition is not just limited to South African savannas (Fig. 2). For example, P limitation can occur at relatively low plant N:P. Exotic C4 grasslands in Hawaii had foliar N:P of 2.3 and were shown to be primarily limited by N, which itself supports the use of the thresholds (D’Antonio & Mack, 2006). Yet, after N fertilization, biomass in the D’Antonio & Mack study increased with additional P, but foliar N:P of the vegetation fertilized with N was only 4.3. Such a low N:P would generally be considered to indicate N limitation. Similarly, N limitation can occur at relatively high N:P in grasslands. In a Venezuelan savanna, aboveground grass production was primarily limited by N, yet grass foliar N:P was 23 (Barger et al., 2002). Co-limitation between N and P at low N:P can be found above the lower range of 10 suggested by Güsewell, from 11.3 in a Greek grassland (Mamolos et al., 2005) to 10.8 in grasses of an Amazonian secondary forest (Davidson et al., 2004). Yet, just like at KNP, co-limitation occurs below this lower threshold: 6.6 in both a calcareous European grassland and a semi-arid Australian grassland (Tupper, 1978; Niinemets & Kull, 2005) and 8.2 for a Tanzanian savanna (Ludwig et al., 2001).
Figure 2. Nutrient limitation and distribution of observed nitrogen:phosphorus (N:P) ratios for unfertilized vegetation for this study (M, Makhohlola; S, Satara; N, Nwashitsumbe; L, Letaba; P, Pretoriuskop), and other published studies in grasslands that had included both biomass and N:P data (1, D’Antonio & Mack, 2006; 2, Barger et al., 2002; 3, Mamolos et al., 2005; 4, Niinemets & Kull, 2005; 5, Ludwig et al., 2001, with superscript O referring to vegetation in open grasslands and T referring to herbaceous vegetation under trees). Letaba and Niinemets & Kull (2005) data are offset because they had similar N:P ratios. The position on the x-axis indicates the N:P of unfertilized vegetation. Solid vertical lines are thresholds from Koerselman & Meuleman (1996); dashed vertical lines are thresholds from Güsewell (2004). Inclusion in N, NP, and P rows indicates limitation by N, N and P, or P, respectively.
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The results of this study and previously published ones are insufficient to reject the utility of N:P in predicting limitation in grasslands, yet there is currently more evidence that suggests that N:P ratios will not predict limitation in grasslands than there is evidence that suggests that it will. It is possible that there is a lower threshold for N limitation at the KNP sites than currently suggested thresholds, but even unfertilized plots with an N:P of 3.2 at Makhohlola, which is close to the lower bound of N:P seen in terrestrial vegetation (Sterner & Elser, 2002), were co-limited by N and P. Instead this research suggests that there might be no threshold that consistently separates N limitation and co-limitation by N and P in grasslands.
Examining the patterns of biomass response to factorial fertilization at KNP suggests that co-limitation might have been caused by the ratio of supplies being equivalent to the ratios demanded by plants for optimal growth. When production responds to the addition of two nutrients individually, plants are probably facing tradeoffs in how they allocate biomass or a common limiting nutrient (Bloom et al., 1985; Gleeson & Tilman, 1992). For example, nutrients might differ in availability between two layers of soil, creating tradeoffs in where biomass is allocated in the soil and which nutrients are acquired. When either nutrient is added, productivity increases as resources are allocated away from acquisition of the one co-limiting nutrient to acquisition of the other, leading to greater total resource acquisition and productivity. Alternatively, when productivity only responds to the addition of two nutrients when they are added together, (a) the two nutrients are probably supplied to unfertilized vegetation at the same ratio as demanded by plants and (b) acquisition costs for the two resources are not separate. Without tradeoffs, adding one of the two limiting resources only leads to accumulation of the added resource as both need to be added to stimulate production. At KNP, with biomass primarily responding to the addition of N and P together rather than individually, it is more likely that across the five sites N and P were generally supplied in similar ratios to those required by plants, implying that the plants must have a low optimal N:P.
The low N:P of KNP grasses supports the idea that optimal biomass N:P might not be well constrained among species (Townsend et al., 2007), with species differing widely in their N:P ratio when growth is optimized. For KNP grasses to have a low optimal N:P, they must have either low N requirements or high P requirements compared with other plants. Grasses with the C4 photosynthetic pathway could have lower N requirements than C3 grasses, lowering optimal N:P. The consistency over time in low N:P reduces the probability that P concentrations are high as a result of storage. High P concentrations also are unlikely to be attributable to P-containing metabolites with secondary function such as defensive chemicals or osmoticants (Lambers et al., 1998). Although similar classes of compounds that contain N can be responsible for causing high N:P, compounds with secondary functions rarely contain P and are unlikely to increase P concentrations. Yet, grasses could still have a high P requirement as their cell walls can be covered with sheets of mineral that contain P and other elements such as calcium and potassium (McManus et al., 1977). Whether the cell wall mineralization explains the high requirement for P (and low N:P) of many grasses, or whether the low N:P can be explained by greater amounts of compounds with primary functions such as RNA, DNA, ATP, or phospholipids (e.g. Chapin et al., 1982) remains to be seen. More controlled experiments that identify optimal N:P supply and demand ratios are needed as well as better understanding of how N and P are partitioned among cellular components in unfertilized vegetation such that N:P can be as low as 3.
In addition to understanding the mechanisms that lead to variation in plant optimal N:P, it is uncertain how the ratio of supplies of N and P could consistently be similar to the demands of plants. All other things equal it seems that the odds of the ratios of supplies and demand matching one another would be low. Although some of the matching could be a result of the ratios of supplies promoting species with similar ratios of demand, there are probably additional mechanisms that are constraining the ratio of supplies. For example, variation in P availability might be associated with compensatory N fixation, which would narrow the range of supplies to plants. When P is limiting, N might be more likely to be lost from the ecosystem through denitrification or leaching (Hall & Matson, 2003; Davidson et al., 2004), which would also constrain the ratios of supplies to plants.
Theoretical considerations aside, the presence of co-limitation between N and P at KNP complicates decisions on management strategies. For example, N deposition from upwind power plants is a concern in the park (Dentener et al., 2006). With vegetation co-limited by N and P, N deposition might not directly increase aboveground production. Yet, grass N concentrations might still increase with N deposition, which could benefit herbivores. Longer time-scales of analysis would help determine if plant species composition would be altered by increases in nutrient availability, while experiments that included woody vegetation would provide a more complete picture of the response of the ecosystems of KNP.