Composición geoquímica de sedimentos superficiales alrededor del ecosistema arrecifal de Isla de Sacrificios, Veracruz, México
Leticia Rosales–Hoz,1 Juan Jose Kasper–Zubillaga,1 Arturo Carranza– Edwards1* y Omar Celis Hernández1
1 Instituto de Ciencias del Mar y Limnología, Universidad Nacional Autónoma de México. Apdo. Postal 70305 México 04510, DF. México. *Dr. Arturo Carranza Edwards dr.arturo.carranza@gmail.com Tel. : 56225692
Recibido: 2 de septiembre de 2007.
Aceptado: 15 de octubre de 2008.
ABSTRACT
Twenty three surface sediment samples were collected in the area surrounding the Isla de Sacrificios located in the southwestern Gulf of Mexico. The temporal impact of natural discharges in the area was evaluated through the study of the textural and chemical characteristics of the sediments that surround the Veracruz Reef System. The particle size during the three sampled seasons was associated with the prevailing energy conditions. The degree of influence of terrigenous sediments was evaluated through the content of Al2O3, SiO2, Na2O and K2O, which is higher in October (2004) compared to June (2004) and/or February (2005) due to the rainy season. It was observed that gravel, CaO and CO3 were significant variables grouped in Factor 1 that suggested that gravel–sized fractions are produced by the abrasion of the reef in February (2005) and being correlated with other variables in June (2004). Another groupings were among SiO2, CaO, K2O, CO3, for October (2004) which suggested dilution of carbonates due to the terrigenous input. In addition, the factor analysis showed that grain size and heavy minerals represented by TiO2, MnO, MgO and Fe2O3 have a major importance in February (2005) associated with fluvial discharges. The factor analysis showed that the sedimentological and geochemical characteristics of the sediments varied throughout the different seasons. A correlation among Al2O3 and Na2O, P2O5, y Fe2O3 and organic carbon in the three sampling seasons suggested that these chemical components have a terrigenous source.
Keywords: Reef, terrigenous, sediments, Gulf of Mexico.
RESUMEN
Se estudiaron veintitrés muestras de sedimento superficial, colectadas en los alrededores de la Isla de Sacrificios, ubicada al suroeste del Golfo de México. El impacto temporal de las descargas naturales fue evaluado a través de las características texturales y químicas de los sedimentos que rodean al SAV. El tamaño de partículas de los sedimentos en las tres estaciones del año estuvo en función con las condiciones de energía prevalecientes en la zona. El grado de influencia de los sedimentos terrígenos se determinó por el contenido de Al2O3, SiO2, Na2O y K2O, siendo mayor en octubre (2004) que en febrero (2005) o junio (2004) y estuvo asociado con la temporada de lluvias. Se observó que la grava, CaO y CO3 fueron variables significativas agrupadas en el Factor 1 en octubre (2004) lo cual sugirió que las fracciones tamaño grava fueron posiblemente originadas por la abrasión del arrecife en febrero (2005) reflejando su relación con otras variables para Junio (2004). Otras agrupaciones fueron observadas entre las variables SiO2, CaO, K2O, CO3 lo cual indicó que la dilución de carbonatos es por influencia de terrígenos. El análisis factorial mostró que el tamaño de grano y minerales pesados representados por TiO2, MnO, MgO y Fe2O3 tuvieron una mayor importancia en febrero (2005) asociados con descargas fluviales. Al análisis factorial reflejó que las características sedimentológicas y geoquímicas de los sedimentos varían estacionalmente. La correlación entre Al2O3 y Na2O, P2O5, y Fe2O3 y carbón orgánico sugiere que estos compuestos químicos tienen una fuente terrígena.
Palabras clave: Arrecife, terrígeno, sedimentos, Golfo de México.
INTRODUCTION
]]> Coral Reefs in the southwestern Gulf of Mexico at Veracruz are well–developed environments of reef islands or barriers close to the coastline. Coral reefs are sensitivities to sediment discharges, sea–water temperature and salinities changes, and global warming effect (Shen & Boyle, 1988; Linn et al., 1990; Allison, 1996; Ramos et al., 2004). The Veracruz coastal area is characterized by the presence of the Veracruz Reef System (VRS) that apparently has been subjected to an environmental impact due to natural river discharges of terrigeneous sediments and industrial activities.Additionally, untreated sewage coming from domestic and industrial sources which carry organic carbon, nutrients, and heavy metals is affecting the preservation and life of the VRS (Ramos et al., 2004).
The aim of the present work is to analyze the degree of influence of terrigenous discharges in the area in superficial bottom sediments surrounding the VRS based upon the texture and chemistry of the sediments. The importance of this paper is to highlight the effect that the presence of terrigenous input may have in the VRS.
STUDY AREA
The VRS is located along the coast of Veracruz, southwestern Gulf of Mexico, Mexico. The northern region of the VRS comprises 10 reefs located in front and south of the Port of Veracruz respectively. In present time, the VRS has unfavorable conditions for reef development due to its closeness to the Port of Veracruz and to river discharges that carry important amounts of water. For instance, La Antigua River is located on a basin of 2 880 km2 with an annual average volume of 2,817,000 m3. Another fluvial systems like the Jamapa River, located on a basin of 3350 km2 has an average annual drain of 1,895,000 m3 and the Papaloapan River on a basin of 39,189 km2 has an average annual volume of 39,175,000 m3 (Tamayo, 1991). It seems that these fluvial systems have an impact in the development and preservation of the VRS (Rivera–Ramirez, 2007).
At the Northern portion of the VRS is located the Isla de Sacrificios (19°10' 27" N; 96° 05' 31 W) (Fig. 1) covering an area and perimeter of 53,770 m2 and 917.3 m, respectively and 1.56 km away from the coast. On the other hand, the Isla de Sacrificios Reef has an area and perimeter of 397,630 m2 and 2,745 m respectively.
Depths near the Isla de Sacrificios range from 8 m to 15 m (Fig. 1). Coastal currents surrounding the study area are in average 3 cm s–1 with northwesterly and easterly components in winter and summer respectively (Fernández–Eguiarte et al., 1992 a, 1992 b). Dominant winds come from the north and northwestern part of the Gulf of Mexico with average velocities ranging from 6 m s–1 to 8 m s–1 in February, June and October. Northerly winds dominate more than 60 % of the time in February. The rainy and dry seasons correspond to a period from July to October and from April to May respectively.
MATERIAL AND METHODS
]]> Surface sediments were collected at 23 different sites near the Isla de Sacrificios area. In addition, sediment samples from the Jamapa River mouth were taken in order to have a chemical control over the adjacent land. Three sampling trips were carried out on June (2004), October (2004) and February (2005). Samples were taken with a van veen dredge and sediment samples were removed from the superficial middle part of each sample to avoid the contact of the sediments with the metallic walls of the dredge. Sediments were transferred to plastic bags and kept at 4°C until analysis.The grain size distribution of the sediment samples was determined by means of Coulter LS230 laser equipment. Four granulometric groups were identified: gravel, sand, clay and silt. Mean graphic size (MzΦ) and sorting (σΦ) were obtained following the formulas and limits proposed by Folk (1974).
Sediment samples for chemical analysis were dried at 55°C for 48 hours, and homogenized in a SPEX 8000 mixer/mill using tungsten–carbide vials. Organic carbon was measured by oxidation with potassium dichromate according to the method described by Gaudette et al. (1974). The coefficient of variation of the organic carbon determination was 2.64%. Carbonate was measured by back titration of an excess of hydrochloric acid with sodium hydroxide based on the method by Hesse (1971). The coefficient of variation of carbonate determination was 1.86 %.
Analyses of major elements were made by using an X Ray Fluorescence sequential system, model Siemens SRS 3000. Accuracy of the analyses was measured by the use of reference material the coefficient of variation obtained were: SiO2: 1.18 %. Al2O3: 9.66 %, Fe2O3: 1.88 %, MnO:1.82 %, MgO: 2.0 %, CaO: 3.75 %, Na2O: 1.98 %, K2O: 1.34 %, TiO2: 2.6 % and P2O5 : 5.5 %. Correlations between organic carbon, SiO2, Al2O3 and depth were carried out (Fig. 2) as well as parameters distributions (Fig. 3).
RESULTS AND DISCUSSION
Table 1 shows the textural parameters of the sediments analyzed (grain size (MzO), classification (σΦ) and percentages of gravel, sand, silt and clay.
High MzΦ values correspond with finer sediments (Φ = –log2D (mm)), that usually were deposited in areas with very low energy. The origin of fine sediments may be related both to urban and fluvial discharges.
MzΦ average values presented similar values in the three sampling seasons (Table 1). However, the highest values were observed in October (2004) at sampling points 19 (MzΦ = 4.128), 17(MzΦ = 3.448) and 13 (MzΦ = 3.368). The location of these samples suggests fluvial discharges linked to the rainy season at the basin (Fig. 1).
The highest MzΦ values were observed at sampling points A (MzΦ = 3.460), 13 (MzΦ = 3.249) and 7 (MzΦ = 3.291) in June (2004) whereas sampling points 7 (MzΦ = 3.594), A (MzΦ = 3.346) and 14 (MzΦ = 3.093) presented the highest MzΦ values in February (2005). The proximity of these samples to the Isla de Sacrificios reef suggests low energy conditions in this area allowing the deposition of fine sediments. The area between the Isla de Sacrificio and Pajaros reef is a potential non–exposed region from the northerly winds and high energy of the waves.
]]> The samples collected at Jamapa River Estuary showed an average MzΦ value of 1.29 Φ in June (2004). However, a difference in MzΦ values was observed at sampling points J4 and J5 (Mz = 1.1830 and 5.2360, respectively) in October (2004). Low MzΦ values correspond to coarser grains that were located further to the fluvial mouth, whilst fine–sized samples are imparted by the turbulence of high wave energy as well as by an excess of suspended fine sediments related to the rainy season. The Jamapa River is an important fluvial system in the sediment contribution to the ocean basin and impact in the VRS by terrigenous input due to its closeness to the VRS and its average annual drain of 1,895,000 m3 Furthermore, close to the Jamapa River mouth there is a high concentration value of suspended matter in October (2004) of 17.30 mg/l compared to values between 10.10 mg L–1 to 10.98 mg L–1 in June (2004) (Rivera–Ramírez, 2007).During the northerly wind season (October, 2004), a difference between sites J7 and J6 was observed (J7 = 4.104 Φ and J6 = 2.722 Φ respectively) (Table 1). In this case the fine–sized samples are located in the wider section of the river where water flux losses velocity, heavy suspended load is present and finer sediments settle down into the river bed (Schumm, 1977).
High sorting values (σΦ) were associated with sediment mixing produced by marine and fluvial processes. In this study, sorting values (σΦ) showed similar trends during the three sampling seasons. However, in June (2004) and October (2004) was observed a better sorting (Fig. 3a) in samples close to the shoreline compared with those from February. This suggested that during low wave energy periods sediments tend to be very well sorted as it can occur in June (2004) and October (2004). However, chaotic periods as those linked to the strong cold north winds (locally named "nortes") could produce poorly sorted sediments as it was observed in February (2005) are present.
Poorly sorted sediments were observed between Isla de Sacrificios and Pajaros Reefs. Currents drifts and velocity together with mixing of terrigenous and biogenic sediments may explain the poor sorting of the sediments in this area. Furthermore, well–sorted sediments were observed in June (2004) (0.980 Φ) suggesting probably summer time calm weather conditions (Table 1).
Poorly– sorted values were observed in the estuarine area in February (2004) (2.788 O). In contrast, well–sorted values were identified in October (2004) (0.696 O). These values reflected the variations in the hydrodynamic energy present in the system during winter and fall.
Gravel concentrations varied at different seasons: a) Gravel concentrations in June (2004) at different sampling stations were 11 (0.64%), 19 (3.09 %) and B (7.47%) and in October (2004) showed the following results at different sampling sites: 12 (11.85%), 18 (0.29%) and 19 (0.17%). In February (2005), six sampling points concentrated gravel as follows: 15 (11.04%), 13 (8.46%), 19 (5.21%), B (4.44%), 9 (2.37%), 11 (0.19%). Gravel produced–fractions were likely to occur in February but as it was showed by the factor analysis it was significantly correlated with other variables in June (2004).
Northerly winds with velocities between 6 to 8 m s–1 may have an effect in the coralline structures near the Isla de Sacrificios that causes the breaking of the reef and the generation of carbonate–terrigenous mixed gravels in high energy marine environments. This interpretation is supported by the factor analysis for June (2004) where gravel and CaO are grouped in Factor 1 (Table 3).
Results showed that average sand concentration was higher in February (2005) (98.89 %) compared to those observed in June (2004) (91.34 %) or October (2004) (87.54 %) due to fluvial discharges caused by rains and "nortes" in February. Sampling sites with the highest values in February (2005) were at 1, 3, 5, 8 10, 11 and 16 points. In June (2004), the higher sand values were at sampling sites 5, 6, 9, 11, 15, 16, and 21. In addition, the Jamapa River showed similar concentration values to those observed near the Isla de Sacrificios in June (2004). Sand concentration nearshore was probably associated with stable wave regime and homogeneous distribution of sand along the shore. In October (2004), high sand concentration values were present in sampling sites 9, 10, 11, and 16. The Jamapa river showed two dissimilar sand concentration values J4 = 96.69 % and J5 = 34.00 % in October (2004) whereas the river showed higher concentration values at site J6 (69.86 %) compared to site J7 (45.85%) in February (2005). Low concentration sand values in October (2004) was linked to the Jamapa River discharges that produce fine sil–clay fractions deposited to the southeastern part of the Isla de Sacrificios Reef.
]]> From the preceding results, it can be said that the highest concentration of sand was located close to the coastline suggesting terrigenous input (75% to 77%) by fluvial discharges especially around the Jamapa River close to the Port of Veracruz (Fig. 3c).Furthermore, the silt + clay fraction increased with water depth where low wave energy allows mud deposition but also due to the discharges of the Jamapa River in October (2004). The silt + clay distribution pattern is similar during June (2004) and February (2005); coarse and fine–sized grains were closer to the coast and the reefs respectively. High silt + clay concentration values were located at sites 13, A, 7 and 14 suggesting low energy hidrodynamic conditions in these sites.
In the river area, samples collected in June (2004) show very low fine–grained concentration at the three sampling points. However, during October (2004), sample J5 (Fig. 1) shows High amounts of silt + clay (66.00 %) in the Jamapa River indicated the control that the wet season exerts over the sedimentological characteristics of the fluvial network and ocean basin.
The average major elements concentrations of the samples during the three sampling periods perform were summarized in Table 2. SiO2 was the most abundant major element, ranging from 14.79 to 67.87 %. SiO2 concentration was higher in the river than in the shelf sediments, where the highest values were located in sediments near the coastline (Fig. 2b) and where most resistant minerals such as quartz withstand the physical weathering due to the energy of the waves and littoral currents. The lowest SiO2 values were found in samples with high carbonate content, usually located to the SE of Isla de Sacrificios. SiO2 lower concentration in February compared to June (2004) and/or October (2004) suggests an homogenization of the sediments associated with "nortes".
Al2O3 concentration was higher in river samples (mean values 16.49 % and 10.23 % respectively) than in shelf sediments (Table 1). This decrease in Al2O3 was due to the presence of carbonates in the area that dilute the terrigenous sediment content. In October (2004), high concentrations of Al2O3 were observed in sampling points 19 and 20 probably linked to the Jamapa River discharges. During the three field trips, the highest Al2O3 values were observed at sampling point 7 that also had high clay and silt concentrations, suggesting that low energy at this point allows the deposition of fine sediments. Al2O3 concentration in sediments near the Great Barrier Reef, Australia shows lower values (8.2 %–9.4 %) (Dunbar & Dickens, 2003) compared to those observed in the Isla de Sacrificios probably due to major input of terrigenous sediments near the Isla de Sacrificios.
Iron concentrations in the coastal area range between 1.85 and 5.81 %. Higher values were observed in October (2004), when the correlation between Al2O3 and Fe2O3 was higher (0.80) compared to June and February (2005) (0.63) suggesting that the amount of Fe2O3 transported associated with Al2O3 was higher. The influence of non–detrital factors on bulk sediment composition can be seen through the distribution of Fe2O3.
A graph of Fe2O3 vs Al2O3 (Fig. 2c) shows three groups of samples based on Fe2O3 concentration: 1) samples with Fe2O3 concentration exceeding that represented by the Fe2O3 / Al2O3 ratio can be used as an approximation of the heavy mineral present in the sediments; samples 3, 4, and B2 located near the coastline and closer to the port entrance, are above the line during the three sampling periods. These samples had high concentrations of MnO, MgO, TiO2, and V; the association of these compounds with Fe2O3 was very high, suggesting that they were present in the form of heavy minerals, 2) samples where Fe2O3 / Al2O3 ratio was relatively constant suggested that the iron was held in structural positions within the alumninosilicates introduced by the terrigenous discharges to the area, 3) samples with Fe2O3 concentrations lower than the average concentration in the area, samples 6, 8, 11, 15, and 16 showed lower Fe2O3 concentrations during the three sampling periods, these samples were enriched in SiO2, which dilutes de iron content of the samples.
The concentration of Fe2O3 in the river samples (range 5.04 %– 6.22 %) was higher than the average found in some other coastal areas (Table 2) near coral reefs like the Great Barrier Reef Platform, Australia (2.63 %–3.19 %) (Dunbar & Dickens 2003). Apparently, the presence of carbonates in coastal area produces a dilution of the Fe2O3 carried by the terrigenous supplies as it was also observed in Australia. Even in core profiles, there was an inverse relationship between CO3 and siliciclastic input. In other words an increase in CO3 there was a decrease in siliciclastic sediments in deep ocean basins near coral reefs (Dunbar et al., 2000; Dunbar & Dickers 2003).
A negative significant correlation (Fig. 4) between CaCO3 and Fe2O3 was only observed for sediments sampled on the rainy (October) season. This is probably due to the fluvial supply of terrigeous sediments: a high value of carbonates is then associated with a low input of sediments in the water column.
Organic carbon concentration (Table 2) showed a gradual increase parallel from the coastline. The lower values were found in the sampling points closer to the coast because wave energy dissipates fine sediments related to organic carbon (Fig. 2a). The higher values were found at sampling points 7 or A in the N part of the studied area. They were associated with fine sediments and high clay and silt content. A value of 1.36 % was found in October (2004) at sampling point 19 closer to the discharge area of Jamapa River which suggested a fluvial origin from the upper basin. High organic carbon values were found in samples located near the harbor entrance in October (2004) and February (2005). The harbor could be the source of the high values found during the three different periods studied at sampling points 7, 13 and A. The organic carbon concentration in the river showed high values (2.28 %) up the river during October (2004). They could be associated with the supplies from the high parts of the basin. The organic carbon concentration in the river samples indicated local discharges with different variations in its concentrations.
]]> The concentration and distribution pattern of CaCO3 at the three different seasons studied experienced a slight change.The sampling point with higher CaCO3 concentration move southwards. The maximum CaCO3 concentration was present in sampling site 13 (47.5%) in February (2004) whereas the maximum concentration observed was in sample "B"(75.2 %) in June. Finally, in October (2004), sample site 18 showed the maximum CaCO3 concentration (66.7 %). Apparently, the terrigenous supply that reaches the area and provides of sediments between Isla de Sacrificios and Pajaros Reef moves CaCO3 concentrations southwards. It has been reported (Carranza–Edwards et al., 2005) that the supply of fine sediments inhibits carbonate precipitation. The CaCO3 concentration in the area has been used as an indicator of the presence of biogenous sediments. The distribution pattern of CaCO3; was shown in Figure 3b. In October (2004), the presence of terrigenous sediment toward the southeastern area was evident.
An R–mode factor analysis was carried out for each season and the whole data using the granulometric and chemical variables (Davies, 1986; Voudouris et al. 1997). This multivariate analysis extracted a number of factors that explain as many of the observed variations from the original data.
Gravel percentage, CaO, Na2O, K2O and CO3 grouped as the most important variables common in June (2004) suggesting that gravel may be originated due to the abrasion of the reef system during the storms related to cold fronts and also during the rainy season. In October (2004) the variables grouped were SiO2 CaO, K2O, CO3 (Table 4) indicating that there is a dilution of carbonates with the presence of terrigenous sediments due to the negative loading value of CaO and CO3 in relation to the rest of the chemical components. In February (2005) there is a relationship between TiO2, MnO, MgO and Fe2O3 (Table 5) that indicated: a) mafic sources containing heavy minerals draining across the continental basement seawards via fluvial discharges and, b) a probable destruction of the reef that provided gravel–sized detritus composed of carbonates since terrigenous sediments are unlikely to be coarse–sized around the reef derived from river or high energy episodes.
When carrying out the factor analysis for the whole of the three seasons data, three factors were retained as significant (Table 6). The most important components were the concentrations of SiO2, CaO, K2O, CO3 with a negative value for CaO suggesting dilution of carbonate content with the presence of terrigenous input.
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Terrigenous sediments, i.e. clastics consisting of material eroded from the land surface included only few basic minerals (quartz, clay minerals, feldspars, muscovite and heavy minerals) (Schulz & Zabel, 2000). With the exception of quartz, complete weathering of metamorphic and igneous rocks leads to the formation of clay minerals. Consequently clays represent, together with quartz, the most important minerals constituent in terrigenous sediments. The main components of clay minerals are Al and Si; Al is also present together with Na, K and Ca, in feldspars. Therefore, the concentration of these elements (Al2O3, SiO2, Na2O, K2O) in coastal sediments was taken as a measure of terrigenous supplies.
A correlation analysis of the studied parameters showed a statistically significant correlation among Al2O3 and Na2O, P2O5, K2O, Fe2O3 and organic carbon in the three sampling seasons suggesting that these chemical components have a terrigenous source. This was also supported by the factor analysis performed for June (2004) and February (2004) in which factor 2 grouped the preceding variables as most significant for the factor loadings (Tables 3 and 5).
The distribution pattern at the three different seasons studied of the sum of Al2O3 + SiO2 + Na2O + K2O + P2O5 (terrigenous index) was shown in Figure 3c. In this study the terrigenous index was a proposal of a measure of the terrigenous influence in the sediments. The influence of terrigenous discharges was more evident during October (2004), when the entrance of sediments with a high terrigenous index was more evident along the coast line. However, terrigenous discharges travel further from the coastline seawards in February (2005).
The prevailing type of sediment in the area in the three different sampling seasons was evaluated through the ratio of the terrigenous index (Al2O3 + SiO2 + Na2O + +K2O + P2O5) against CaCO3 that was taken as having a biogenous origin. Using the average values obtained for this ratio in each sampling trip, a differentiation was made between sites, sampling points that are above the average ratio value are constituted mainly by terrigenous sediments, samples below this value present major influence of biogenous sediments. The terrigenous influence was similar during the months of June and October (Fig. 3d), when carbonated sediments prevailed in the area close to the Isla de Sacrificios. Terrigenous sediments in February (2005) are at higher depths including samples 17 and 14 and carbonated sediments extended from the west of the Isla de Sacrificios landwards possibly due to the influence of the strong northerly winds that affected the reefs located to the north of the studied area.
ACKNOWLEDGMENTS
Thanks are due to the authorities of the Instituto de Ciencias del Mar y Limnologia, UNAM; to DGAPA, UNAM which supported this research through project PAPIIT IN104705–2; to the Secretaría de Marina Armada de Mexico, for their valuable support in sample collection and to Acuario of Veracruz, for their valuable help in the use of their facilities for sample processing. The authors also thank S. Santiago Perez and E. Morales de la Garza for their technical support in the collection and analysis of samples.
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