ATMOSPHERIC
MERCURY CONTAMINATION BIOMONITORING USING EPIPHYTIC BROMELIADS (TILLANDSIA USNEOIDES). CASE STUDY: THE
GOLD SHOPS IN PORTO VELHO, RONDONIA, BRAZIL.
Vergotti, M., Biogeochemical Laboratory, UNIR, vergotti@unir.br
Gali, P.A.S., Biogeochemical Laboratory, UNIR, priscilagali@zipmail.com.br
Bastos, W.R. , Biogeochemical Laboratory, UNIR, bastoswr@unir.br
Silveira, E.G., Biogeochemical Laboratory, UNIR, labmerc@unir.br
Malm, O., LREPF-IBCCF-UFRJ, olaf@biof.ufrj.br
Santos, S.S., Biogeochemical Laboratory, UNIR, labmerc@unir.br
Maniesi, V., Biogeochemical Laboratory, UNIR, maniesi@unir.br
Torres, J.P.M., LREPF-IBCCF-UFRJ, jptorres@biof.ufrj.br
ABSTRACT
The Bromeliad Tillandsia usneoides is an epiphyte that
captures all its nutrients from the atmosphere, and concomitantly accumulates
heavy metals, among them mercury. Systems of two baskets each with T. usneoides were distributed in the
gold shops and the ex-gold shops of the Porto Velho city and recovered after an
exposure of 15, 30 and 60 days. Each compartment of basket contained 5g of
plants previously collected in a clean area with known Hg concentrations.
INTRODUCTION
Goldmining in the
Madeira river basin started around 1978 and grew up to 1985 producing something
like 200 to 300 tons of Gold in the first 10 years. Today this activity is
reduced by a factor of 10 times. During mining process small gold particles are
concentrated and afterwards collected by amalgamation method. In the field
amalgams are first time burnt releasing most of the Hg to atmosphere. At a
later date in the goldshops in Gold trade centers cities a new burning for
purification is releasing the remaining Hg through rudimentary exhaustion
systems, but with indoor contamination also exposing workers as well as
neighbourhood.
OBJECTIVES
·
Introduce the use of biomonitoring indoor air Hg with the bromeliad Tillandsia
usneoides in Amazon region
·
Evaluate the Hg contamination in goldshops and ex-goldshops in Porto
Velho city
·
Verify the Hg absorption by the bromeliad along time for optimising its
use.
MATERIAL AND METHODS
Transplanting technique were applied systems containing two plastic baskets containing around 5g of the plant each. Those systems were exposed in goldshops and ex-goldshops for periods of 15, 30 and 60 days. Air temperature at the shops ranged from 33 ºC to 37 ºC. A waterfall distant 31km from the city was also investigated. After that the plants were washed for particles removal and cut in very fine pieces for homogenising and making digestion easier. Mineralization were performed with strong acid solutions (H2SO4, H2O2 e KmnO4) and heating at water bath at 60 ºC. Hg determination was done by Atomic Absorption Spectrophotometry (Flow Injection Mercury System - FIMS-400, Perkin-Elmer). Samples were prepared and analysed in triplicates. Analytical Quality Control were performed by routine analysis of reference material IAEA-140/TM (Table 3). Results are presented in dry weight basis (mg de Hg.g-1d.w.).
RESULTS
AND DISCUSSION
Hg concentrations
in plants exposed in the all shops presented increasing values along exposing
times (Tables 1 and 2 and figures of different active goldshops). Values
obtained in plants after 30 days exposure in active goldshops showed the
average of 1,24 mg.g-1 that
is 16 times higher than the value observed in control plants and close to the
waterfall. For ex-goldshops we found for the same exposure period the average
value of 0,23 mg.g-1,
that is only 3 times higher than control plants. Those values were much lower
than the ones found by Malm (1998), in the same dry season in goldshops in Alta
Floresta (MT), 4,25 mg.g-1
but with plants exposed for 45 days. This difference should be mainly explained
by the reduced gold production nowadays compared with in 1995/6.
Table 1. Average
Hg concentration in Tillandsia usneoides in the gold shops of the Porto Velho city.
|
Exposure time (days) |
Sample |
Average (mg.g-1) |
S.D. |
|
15 |
3 |
0,80 |
0,29 |
|
30 |
3 |
1,24 |
0,28 |
|
60 |
3 |
2,84 |
0,31 |
Table 2. Average
Hg concentration in Tillandsia usneoides in the ex-gold shops of the Porto Velho
city.
|
Exposure time (days) |
Sample |
Average (mg.g-1) |
S.D. |
|
15 |
2 |
0,20 |
0,03 |
|
30 |
2 |
0,23 |
0,01 |
|
60 |
2 |
0,21 |
0,04 |
Table 3. Average
Hg concentration (mg.Kg-1)
in reference sample.
|
Reference Sample |
Average ± S.D. Our lab. value |
Average ± S.D.
certificate value |
Confidence Interval |
|
IAEA-140/TM |
30 ±
11 |
38 |
32 - 44 |
IAEA=
International Agency of Energy Atomic
CONCLUSIONS
We conclude that
the bromeliad Tillandsia usneoides
can be used for Hg atmospheric biomonitoring in both indoor as well as
outdoor environments. This method allows long term exposure evaluations at
extremely low cost and at an enormous number of places at the same time.
REFERENCE
MALM, O.; Fonseca, M.F.; Hissnauer, P.M.; Bastos, W.R. and Pinto, F.N.
1998. Use of epiphyte plants as bomonitors to map atmospheric mercury in a gold
trade center city, Amazon, Brazil. The
Science of the Total Environment, 213/1-3 pp. 57-64.




Hg concentrations in Bromeliads from different
goldshops along time.