INTRODUCTION
The long pepper (Piper hispidinervum C.DC.), is an endemic Amazon species of high commercial interest due to its safrole production (Gottlieb et al. 1981; Andrade et al. 2009). This secondary compound is classified as a sesquiterpene produced by plant metabolism and used in the chemistry industry to obtain heliotropin and piperonil butoxid, used as fragrance fixers by the cosmetic industries, as synergic agent in bio insecticides and traditional popular use (Maia et al. 1987; Figueirêdo et al. 2004; Sauter et al. 2012). Safrole is considered one of the most used essential oils in the world (Bizzo et al. 2009) and its commercial demand has stimulated research on breeding of long pepper plants, with good yield of essential oil and high safrole content, above the level of 90% required by the industry (Maia et al. 1987; Bergo et al. 2002).
Long pepper is a predominantly alogamous species with high degree of heterozygosis, which directly influences the management and the domestication of the species (Wadt and Kageyama 2004). There is disagreement over chromosome number, however Nunes et al. (2007) states that this is a diploid species (2n = 24), expanding the group of species of the genus Piper with basic number x = 12. According to those authors, this group might be a primitive group from which the x = 13 lineage has evolved. There is evidence of genetic diversity associated with high levels of safrole in native long pepper populations in the Amazon region, with distinct groups within micro regions of Upper and Lower Acre (Wadt and Kageyama 2004; Andrade et al. 2009). Propagation of this perennial species occurs by seeds and cuttings and plants reach 1.60 m to 1.80 m height, with fast growing and harvesting cycle of one to two years, while maintaining oil yield over successive harvest, presenting high capacity of regrowth after cutting and contributing to the sustainability of this activity (Bergo et al. 2005).
Extraction of long pepper essential oil is done after drying the biomass. This process may change the content of volatile compounds, which are sensible to water loss, directly affecting yield and composition of the essential oil (Corrêa et al. 2004; Rahimmalek and Goli 2013). Standardizing the biomass drying process of long pepper under field conditions is difficult since the harvest season take place mainly towards the end of the rainy season (from March to April) in the Amazon region (Bergo et al. 2005; Negreiros and Miqueloni 2013b). Excessive air moisture during this period leads to biomass contamination by microorganisms and increasing labor demand to turn the biomass pile on a daily frequency during four to eight days to the drying process.
The objective of this study was to analyze the yield of essential oil and safrole content of fresh and dried biomass of long pepper accessions maintained in the Active Germoplasm Bank of Embrapa Acre, Brazil, aiming at selecting genotypes with best performance on fresh biomass to recommend to the breeding program of the species.
MATERIALS AND METHODS
The experiment was carried out at the experimental station of Embrapa Acre during 2010, after extraction of essential oil from fresh and dried biomass from 15 populations of long pepper. Samples were collected from the Active Germplasm Bank (AGB) and analyzed in the Laboratory of Essential Oils of Embrapa Acre, in Rio Branco, Acre state, Brazil. The city is located at 9o58'22"S, 67o48'40"W (datum WGS 84) and altitude of 160 m. The climate is classified as AWI (hot and humid), according to Köppen classification, with medium temperature of 27 ºC, annual rainfall of 1,940 mm and 80% relative humidity. The soil of the experimental area was classified as an Ultisol (Embrapa 2006), with the following chemical characteristics at a depth of 0.0 - 0.2 m: pH(H20): 4.5; K: 0.1 cmolc kg-1; Ca: 1.0 cmolc kg-1; Mg: 0.3 cmolc kg-1; A1: 1.4 cmolc kg-1; organic matter: 14.0 g kg-1; cation-exchange capacity: 1.8 cmolc kg-1; base saturation: 26%; aluminum saturation: 22%, and P: 4.0 mg kg-1, and the following physical characteristics: sand: 610 g kg-1; silt: 310 g kg-1 and clay: 80 g kg-1.
Planting was conducted in the rainfall period, in a 2 x 2 m arrangement adopting the recommended treatment for this crop species, with three annual weedings, with two before cutting the above ground biomass, between March and April, and one after fertilization based on soil analysis, with annual dressing application of 2 g of P2O5, 7 g of N and 12 g of K2O per plant during January (Bergo et al. 2002).
The experimental design was completely randomized, involving 15 populations with one replication per population. Each replication consisted of a plot with 8 x 22 m and 30 plants in three rows, with two considered border rows and 10 central plants per plot considered for analysis, in a total of 15 plots and 150 individuals.
Open pollinated populations of long pepper (Piper hispidinervum C.DC., Piperaceae) were initially collected in 2000 in the Valley of Acre, in the eastern region of the Acre state, Brazil, and subsequently established in the Active Germplasm Bank (AGB) of Embrapa Acre. The selection of the population for this study was based on regional representation, with populations derived mainly from the micro region between Rio Branco and Brasiléia, and consisted of a minimum number of 30 individuals per population, and by values of essential oil yield and safrole content commercially satisfactory (above 90%) compared to other populations of the AGB (2000 individuals within 43 populations) observed in previous studies.
For each of 10 individuals in a plot from each population, two samples of aboveground biomass containing leaves and thin branches were collected. One of the samples, corresponding to the fresh biomass, with a mean of 70% moisture was immediately taken to the lab and analyzed while the second sample was taken to a solar drier for a four to six days drying period, being revolved on a daily basis until reaching 10% of moisture (Bergo et al. 2002). Sample of fresh and dried biomass were analyzed for moisture and safrole content, and yield of essential oil.
Biomass's moisture content (%) was determined in order to calculate yield in moisture free basis (MFB). This moisture content was based on the principle of the immiscibility of the solvent (toluene) and the water from fresh and dried biomass (Figueirêdo et al. 2004). Six grams of fresh biomass and 5 g of dry biomass were chopped and put, separately, inside a 250 ml round bottom flask. The flasks were connected to a Dean-Strak apparatus combined with a reflux condenser. Then, 80 ml of toluene were added through the top of the condenser, in order to allow the backflow to the flask, which was heated at 120 ºC, and the water content extracted from the biomass was recorded.
Yield of the essential oil (%) was calculated based on fresh and dry biomass in the moisture free basis (Santos et al. 2004). This method was used to determine the content of essential oil in MFB and the result was expressed in percentage, corresponding to volume/weight of the essential oil from the fresh and dry biomass. The results were obtained based on laboratory conditions.
For determination of safrole content (%), the essential oil was extracted by the method of cohobation or recirculation of condensed water (Heath 1977). Extraction was based on 90 g of fresh biomass and 35 g of dried biomass, for each individual from the 15 populations. The samples were mixed with 450 ml of distillated water and subjected to the water boiling temperature in a heating mantle for 60 min for the dried biomass and 180 min for the fresh biomass. At the end of this period, the oil was collected and quantified in a gas cromatograph (6890, HP, Palo Alto, CA, USA) using Helium as the carrier gas and equipped with a flame ionization detector and capillary column of 30 m length and 25 mm internal diameter. The internal injector and detector were maintained at 250 °C with reduced injection volume (split of approximately 1:100). The initial oven temperature was maintained at 80 °C for 10 min with increment of 4 °C per minute to 140 °C with subsequent increase of 20 ºC per minute until the maximum temperature setting of 260 ºC (Figueiredo et al. 2004).
The variables essential oil yield (in MFB) and safrole content obtained for each of the 10 individuals per population were submitted to analysis of variance (ANOVA), considering each population as the treatment in separated analyzes. After that, when the ratio maximum to minimum experimental error mean square was less than seven (i.e. MSEmax/MSEmin ≤ 7.0) a joint analysis of experiments was performed (Pimentel Gomes 1987, Neves et al. 2006). The means for type of biomass (fresh and dried) of each population were compared by Student's t-test, at 5% of probability. The analyzes were performed using Sisvar 5.3 (Ferreira 2008).
RESULTS
For oil yield the ratio of the maximum to minimum experimental error mean square was 6.27, whereas, for the safrole content the MSEmax/MSEmin ratio was 7.45. Thus, it was only possible to make comparison for essential oil yield among populations. Populations 12, 2, 10, 1 and 11 were not different of populations 9, 15 and 13, but differed from the remaining populations in fresh biomass. For dry biomass populations 14, 11 and 9 differed only population 1, 8, 5 and 4 (Table 1).
Table 1 Means of fifteen populations (± standard deviation) of long pepper for essential oil yield based on the condition of analyzed biomass (fresh or dried), Rio Branco, Acre, Brazil.

Populations 4, 5, 9, 11, 13 and 15 showed no difference in essential oil yield in relation to the type of biomass. Populations 1, 2, 10 and 12 showed higher yield of essential oil on fresh biomass. All of these populations, except for populations 4 and 5, showed yields above 4%, which is considered satisfactory for the industry. The remaining populations showed better performance on dried biomass, with values of yield on fresh biomass below 3.4%. For dried biomass, populations 14, 9 and 11 showed yields above 4%, with lower variation than on fresh biomass (CV of 13.18% for dried biomass and 29.74% for fresh biomass), indicating a more homogeneous material after drying.
For content of safrole, populations 5, 8, 9, 10, 12 and 15 showed no difference on type of biomass (Table 2). These populations, except population 14, had safrole content values above 87%, considered satisfactory for the industry. For dry biomass, only population 1 showed value below 80%. The variation on this type of biomass was also lower than on fresh biomass (CV 4.53% and 8.18%, respectively).
Populations 5, 9, 10, 12 and 15 showed no differences between types of biomass for both characteristics, essential oil yield and safrole content, and these populations, except 5, were the ones that showed higher performance for all characteristics, according to the values required by industry especially for safrole content, based on fresh biomass.
DISCUSSION
The influence of the drying process on yield and composition of the essential oil has been observed on several species, generally increasing yield and major component content (Corrêa et al. 2004; Sellami et al. 2011; Rahimmalek and Goli 2013). The variability of essential oil yield of long pepper populations (Table 1) is high, which indicates the possibility of genetic gains, as noted by Negreiros and Miqueloni (2013a) for long pepper. On the other hand, safrole content shows a higher degree of homogeneity. This variability was observed by Gottlieb et al. (1981) , Bergo et al. (2005)and Estrela et al. (2006), who reported 3 to 5% of oil yield on dried biomass of long pepper and 80 to 90% of safrole content in the individuals from the Amazon region and Andrade et al. (2009) observed oil yield of 0.9% and safrole content of 18.4% in Mato Grosso state, Brazil.
As expected, the values of essential oil yield and, specially, safrole content are higher in extractions on dried biomass compared to fresh biomass. In some populations of long pepper, safrole did not suffer significant reductions in essential oil on fresh biomass when compared to dry biomass. This indicates that, in some genotypes, the main composition of the essential oil is not influenced by the drying step used for extraction. This trend has already been observed in Piper aduncum by Negreiros and Miqueloni (2013b) in germoplasms from the Western Amazon.
This differential response is attributed to the loss of minor volatile compounds during the drying of the aboveground biomass, thus increasing the concentration of the major oil component (Smith and Kassim 1979; Santos et al. 2013). Azian et al. (2004) observed that the drying of Zingiber officinale before extraction of the essential oil promoted the rupture of parenchyma's cell walls, facilitating the release of the oil and the oil resin in the adjacent tissues thus, increasing the yield. Oil yield is also influenced by the amount of biomass used for extraction, resulting in a more efficient moisture removal when working with smaller quantities of biomass. Braga et al. (2005), in studies with long pepper, observed yields of 0.2 to 1.3% on fresh biomass while these values practically double on dry biomass.
However, in this study some populations showed higher values for extraction on fresh biomass (Table 1), which can be mainly attributed to the genetic constitution of the germoplasm, which probably has a lower content of volatile compounds. The content of major component, safrole, was not affected by the drying process (Table 2). Rohloff et al. (2005) also observed that the drying process has little influence on the oil peppermint (Mentha x piperita L.), which allow the elimination of the drying process, thus reducing costs for obtaining the essential oil.
Increasing the moisture content leads to the opposite effect by reducing the safrole content, possibly due to the maintenance of volatile compounds in the essential oil (Smith and Kassim 1979; Braga et al. 2005; Costa et al. 2013). This effect is probably due to the maximum gene expression in the fresh biomass and the reduced the variability of individuals in dry biomass, since there was no standardization of plant material by the drying process. Arrigoni-Blank et al. (2010)also observed that there are no differences in yield and content of the major compound of the essential oil predominant on Hyptis pectinata, between dried or fresh biomass samples, also suggesting the influence of the genetic material.
Each genotype responds in a different way to environmental conditions and to the drying process, which removes the water by increasing the percentage of active principles in relation to plant weight (Arrigoni-Blank et al. 2010; Santos et al. 2013). In some herbs, many compounds of interest are lost during drying, due to high humidity, especially in the oil glands of leaves which are dried and the essential oil is carried out by diffusion of the moisture, causing loss of aromatic compounds (Martinazzo et al. 2010).
In addition to that, in the Amazon region, the harvest period of long pepper (towards the end of the rainy season) creates favorable conditions for contamination by microorganisms of the biomass used for extraction of essential oil due to the high air humidity, characteristic of the season. It also results in higher labor costs and resources employed in this step of the extraction process.
These results indicate that some populations of long pepper have good potential for extraction of essential oil with no need of biomass drying, as they suggest that there are no differences on yield of essential oil and safrole content in these populations, when extracted from fresh or dried biomass. Yield of essential oil was higher on dried biomass, however the values of yields obtained on fresh biomass were above 4%, minimum required by the industry to be considered feasible for processing. Populations 9, 10, 12 and 15 showed satisfactory values, for oil yield and safrole content, indicating that the drying process is not indispensable for the extraction of essential oil from these populations.