The OC in AG soils was higher than in AFG, but the OC in the PM10 was
similar (between 3 and 3.3 %) (Fig. 1). The OC in RRI was higher than
in RRO, but the OC in the PM10 was similar (between 1.9 and 2.2 %)
(Fig. 1). The OC content in PM10 emitted by agricultural soils (AG and
AFG) was between 1.3 and 1.7 higher than that emitted by rural roads
(RRI and RRO). To our knowledge, this is the first report of the OC
content in the PM10 emitted by rural roads. The OC contents in the PM10
emitted by rural roads is valuable information to quantify the OC losses
from the soil and the OC discharges into the atmosphere by dust
emission. In semiarid pampas, actual PM10 emission per unit of area of
rural roads was 400 times higher than PM10 emission of agricultural
soils (Ramirez Haberkon et al., 2021).
Figure 1. Contents of organic carbon (OC) in soil and in PM10. AG:
agricultural soils for grain production (n=9); AFG: agricultural soils
for forage and grain production (n=9); RRI: rural roads inside farm
fields (n=9); RRO: rural roads outside farm fields (n=9). Different
lowercase letters indicate statistical differences between land
management systems (p<0.05). Bars represent standard
deviations.
The OC in the PM10 was associated to the OC in the soil. This
relationship was described by a quadratic function (Fig. 2), suggesting
that OC was accumulated in PM10 until reaches a maximum. The maximum OC
in the PM10 was 3.5 % and it was reached in soils with more than 1.3 %
OC. This relationship has not been explored in previous studies for
PM10, but it was explored for other soil fractions. In the clay fraction
(particles <2 µm) a maximum OC content was reached when the OC
in the soil was high than 3 % (Jagadamma and Lal, 2010). A limit of
accumulation of OC also was found for particles fraction <20
µm (Hassink, 1997). Our results and those of previous studies suggest
that the OC can be accumulated in the PM10 until a limit (saturation).