Abstract. Chinese grasslands are extensive natural ecosystems that comprise 40 % of the total land area of the country and are sensitive to N deposition. A field experiment with six N rates (0, 30, 60, 120, 240, and 480 kg N ha −1 yr −1 ) was conducted at Duolun, Inner Mongolia, during 2005 and 2010 to identify some effects of N addition on a temperate steppe ecosystem. The dominant plant species in the plots were divided into two categories, grasses and forbs, on the basis of species life forms. Enhanced N deposition, even as little as 30 kg N ha −1 yr −1 above ambient N deposition (16 kg N ha −1 yr −1 ), led to a decline in species richness. The cover of grasses increased with N addition rate but their species richness showed a weak change across N treatments. Both species richness and cover of forbs declined strongly with increasing N deposition as shown by linear regression analysis (p < 0.05). Increasing N deposition elevated aboveground production of grasses but lowered aboveground biomass of forbs. Plant N concentration, plant δ 15 N and soil mineral N increased with N addition, showing positive relationships between plant δ 15 N and N concentration, soil mineral N and/or applied N rate. The cessation of N application in the 480 kg N ha −1 yr −1 treatment in 2009 and 2010 led to a slight recovery of the forb species richness relative to total cover and aboveground biomass, coinciding with reduced plant N concentration and soil mineral N. The results show N deposition-induced changes in soil N transformations and plant N assimilation that are closely related to changes in species composition and biomass accumulation in this temperate steppe ecosystem.
Abstract. Vehicle emissions have been identified as an important urban source of ammonia (NH3). However, there are large uncertainties regarding the
contribution of vehicle emissions to urban NH3 budgets, as well as the role of NH3 in spatiotemporal fine particulate matter (PM2.5)
formation and nitrogen (N) deposition patterns. The N stable isotopic composition (δ15N) may be a useful observational constraint
to track NH3 emission sources and chemical processing, but previously reported vehicle δ15N(NH3) emission signatures
have reported a wide range of values, indicating the need for further refinement. Here we have characterized δ15N(NH3)
spatiotemporal variabilities from vehicle plumes in stationary and on-road measurements in the USA and China using an active NH3
collection technique demonstrated to accurately characterize δ15N(NH3) on the order of hourly time resolution. Significant
spatial and temporal δ15N(NH3) variabilities were observed and suggested to be driven by vehicle fleet composition and
influences from NH3 dry deposition on tunnel surfaces. Overall, a consistent δ15N(NH3) signature of
6.6±2.1 ‰ (x‾±1σ; n=80) was found in fresh vehicle plumes with fleet compositions typical
of urban regions. Our recommended vehicle δ15N(NH3) signature is significantly different from previous reports. This difference
is due to a large and consistent δ15N(NH3) bias of approximately −15.5 ‰ between commonly employed passive
NH3 collection techniques and the laboratory-tested active NH3 collection technique. This work constrains the
δ15N(NH3) urban traffic plume signature, which has important implications for tracking vehicle NH3 in urban-affected
areas and highlights the importance of utilizing verified collection methods for accurately characterizing δ15N(NH3) values.
Increased nitrogen (N) deposition will often lead to a decline in species richness in grassland ecosystems but the shifts in functional groups and plant traits are still poorly understood in China. A field experiment was conducted at Duolun, Inner Mongolia, China, to investigate the effects of N addition on a temperate steppe ecosystem. Six N levels (0, 3, 6, 12, 24, and 48 g N/(m 2 ⋅a)) were added as three applications per year from 2005 to 2010. Enhanced N deposition, even as little as 3 g N/(m 2 ⋅a) above ambient N deposition (1.2 g N/(m 2 ⋅a)), led to a decline in species richness of the whole community. Increasing N addition can significantly stimulate aboveground biomass of perennial bunchgrasses (PB) but decrease perennial forbs (PF), and induce a slight change in the biomass of shrubs and semi-shrubs (SS). The biomass of annuals (AS) and perennial rhizome grasses (PR) accounts for only a small part of the total biomass. Species richness of PF decreased significantly with increasing N addition rate but there was a little change in the other functional groups. PB, as the dominant functional group, has a relatively higher height than others. Differences in the response of each functional group to N addition have site-specific and species-specific characteristics. We initially infer that N enrichment stimulated the growth of PB, which further suppressed the growth of other functional groups.
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