Zulin Zhang - Royal Society of ChemistryZulin Zhang . Short- and Long-term Temporal Trend of Organic...
Transcript of Zulin Zhang - Royal Society of ChemistryZulin Zhang . Short- and Long-term Temporal Trend of Organic...
Zulin Zhang
Short- and Long-term Temporal Trend of Organic Contaminants in Soils
Following Single or Multiple Applications of Sewage Sludge to Pastures
Global Chemicals Overview • Chemicals are an integral part of
modern daily life. • Global production: 1 MT to 400 MT
between 1930 and 2000. • Global chemical output value:
US$4.12 trillion in 2010. • Over 143,000 chemicals registered in
EU of 2011 (> 1000 t or highly hazardous).
• The growing rate is over 25% between 2012 and 2020 (Table 1).
• Over 50% of total production with environmentally harmful compound .
Emerging Organic Contaminants: POPs and EDCs
Persistent Organic Pollutants (POPs): •Persist in the environment. •Long-range transport. •Bio-accumulate through the food web. •Pose a risk of causing adverse effects to human health and the environment.
Endocrine disrupting chemicals (EDCs): •Substances may interfere with normal function of the endocrine (hormone) system of humans and animals.
Effects on Animal and Human ?
Eggshell thinning in birds of prey
Reduction in frog population
Adverse effects on fish reproduction and development
Development of male sex organs in female marine animals such as whelks and snails
Declines in the numbers of males born
Reductions in male fertility
Female reproductive diseases
Earlier puberty
……
Disposal of Sewage Sludge
EU 27 member states: > 10 M tons (dry solids) annually, rise to 13 M tons of 2020.
Agricultural application as fertiliser
Incineration
land filling
Compost
Others… 41%
19%
17%
12%
11%
EU - 27
Agricultural Use Incineration Landfill Compost Others
Agricultural use of Sewage Sludge in EU and Worldwide
EU 27: >40% sludge applied to land.
EU 7: >50%, UK, France, Ireland, Spain, Slovakia, Portugal and Denmark.
EU 6: <1%; Not authorised to use: Romania, Belgium (Brussels and Flemish region). <1%: Greece, Netherlands, Slovenia.
USA: >7.1 M tons (dry solids), >60% applied to land.
China: 30 M tons, 10-15% applied to land.
Land Application of Sewage Sludge: Benefit and Concern
Benefit
Low cost for the disposal of sewage sludge. Recycling plant nutrients: P, N, S, K, Cu, Zn… Improved soil organic matter, structural properties and soil
moisture retention. Return carbon to soil and reduce in the atmosphere.
Concern
Pathogens Heavy metal Organic contaminants Accumulation in soils and transfer to plants and grazing
livestock and soil invertebrates Evaporate and transport to air, surface and groundwater
Organic Contaminants in Sewage Sludge and Soils
Bisphenol A
Polycyclic aromatic hydrocarbons (PAH)
Polybrominated diphenyl ethers
(PBDE)
Alkyl phenols (detergents)
Plastics – (phthalates)
Dioxins Polychlorinated biphenyls (PCB)
Pesticides
Pharmaceuticals
Bisphenol A (BPA)
BPA: 2,2-Bis-(4-hydroxphenyl)propane
(CH3)2C(C6H4OH)2.
BPA: used as plastics and epoxy resins. e.g. baby and water bottles, food and beverage cans, sports equipment, lining water pipes; thermal paper…
Global consumption of BPA: > 5.5 M tons in 2011.
BPA found in 96% of US pregnant women of 2011 study.
BPA in sewage sludge: low µg/kg – mid mg/kg (dw).
The Debate over BPA Safety
Previous study: Low estrogenic activity compared with estradiol.
Recent works: As effective as estradiol in triggering some specific receptor responses.
European Commission's Scientific Committee on Food, the EU's European Chemicals Bureau, and the US FDA: current levels of BPA present no risk.
American Medical Association, Experts in the field of endocrine disruptors etc: the entire population may suffer adverse health effects from current BPA levels.
US FDA (2012), EU (2011) and Canada (2008) banned the use of BPA in baby bottles while still use in other products.
Glensaugh Research Station
Hartwood Research Station
3 plots: treated 3 plots: control 1 yr treatment
2 plots: treated 1 plot : control >13 yrs treatment
Treated: 2.25 tonnes sewage Sludge per hectare
Control: 225 kg of Inorganic Fertiliser (N) per hectare
Both sites treated with the sludge from the same WWTP
Experimental - (Study 1: Glensaugh; Study 2: Hartwood)
Experimental – Analytical Methods
Zhang et al (2011)
GC-MS
Selective Pressurized Liquid Extraction (SPLE)
Concentration of BPA in Sewage Sludge
Sample Source BPA (ng/g,dw) Reference
Granada, Spain 5-680 Dorival-Garcia et al., 2012
Gran Canaria, Spain 1.4-54.9 Vega-Morales et al., 2011
Greece 620 Gatidou et al., 2007
Germany 4-1363 Fromme et al., 2002
South California, USA 66-217 Yu and Wu, 2012
USA 4600 Kinney et al., 2008
Ontaria, Canada 4-74 Chu et al., 2005
Scotland, UK 636 This Study
Zhang et al (2015)
BPA changes in Sewage Sludge Amended Soils – Study 1 (Glensaugh, Single Application)
Zhang et al (2015)
BPA changes in Sewage Sludge Amended Soils – Study 2 (Hartwood, Multiple Applications)
Zhang et al (2015)
Other studies on organic contaminants changes in sludge-amended soils
PCB burdens of sludge amended plots closely followed that of the control in short-term experiment (Alcock et al., 1995)
The sludge-amended soils (over 20 years of treatment) contained over 5 times more total PCBs than the control plot (Alcock et al., 1995)
Chlorobenzenes in both control and sludge-amended soils were very low and almost indistinguishable in the short term study (Wang et al. 1995)
All the Chlorobenzenes in the sludge-amended soil (over 20 years of treatment) increased and remained higher than those in the control even after sludge application ceased (Want et al., 1995).
Similar to that found for PPBDEs in other study (Eljarrat et al., 2008)
Mean soil concentrations of other OCs in sewage sludge treated soils (Single Application, Glensaugh)
Rhind et al (2013)
Mean soil concentrations of other OCs in sewage sludge treated soils (Repeated Application, Hatwood)
Rhind et al (2013)
Partitioning equilibrium of BPA within the three-phase by Fugacity Model
Zhang et al (2015)
Results of the plant uptake and human exposure by Fugacity Model
Zhang et al (2015)
Estimation of Estrogenicity
EEF = EC50E2 / EC50compound ---------- (1)
EEQ = EEF × Ccompound ---------- (2)
- EEF: Estradiol Equivalent Factor
- EEQ: Estradiol Equivalent Concentration (EEQ)
(Stahlhut et al., 2009)
The number of unshelled mud-snail obviously increase at 1 ng/g EEQ level (Duft et al., 2003).
Estrogenicity of BPA EEF=0.0066 E2 ?
0.00
0.01
0.02
0.03
0.04
0.05
0.06
0.07
0.08
0.09
25/08
/2010
17/09
/2010
30/09
/2010
22/10
/2010
05/11
/2010
18/11
/2010
07/03
/2011
17/03
/2011
04/04
/2011
19/04
/2011
04/05
/2011
18/05
/2011
Date
EE
Q (n
g/g)
CT
0
0.2
0.4
0.6
0.8
1
1.2
2009-4-2
2009-5-27
2009-8-5
2009-8-31
2009-9-22
2009-10-21
2009-11-19
2009-12-21
2010-2-10
2010-3-17
2010-5-26
2010-7-15
2010-8-10
D ate
EE
Q (n
g/g) C
T1T2
Single Application Multiple Application
Only 1 multiple treatment sample over 1 ng/g.
Balaguer et al. 1999; Pillon et al.2005
Estrogenicity of BPA EEF ≈ E2?
0.001.002.003.004.005.006.007.008.009.00
10.0011.0012.00
25/08
/2010
17/09
/2010
30/09
/2010
22/10
/2010
05/11
/2010
18/11
/2010
07/03
/2011
17/03
/2011
04/04
/2011
19/04
/2011
04/05
/2011
18/05
/2011
Date
EE
Q (n
g/g)
CT
Single Application Multiple Application
Control: 72% > 1ng/g Treated: 100%: > 1ng/g
Control: 76% > 1ng/g Treated: 100%: > 1ng/g
Stahlhut et al., 2009
0
20
40
60
80
100
120
140
160
180
2009-4-2
2009-5-2
7
2009-8-5
2009-8-3
1
2009-9-2
2
2009-10-2
1
2009-11-1
9
2009-12-2
1
2010-2-1
0
2010-3-1
7
2010-5-2
6
2010-7-1
5
2010-8-1
0
D ateC
on
cen
trat
ion
(ng
/g)
C
T1T2
On-going Work
Effect of Bulky Organic Fertilisers on Amended Soils
On-going Experiment Glensaugh: Laundry field Long-term (aims: >10 years) Initiate: Sept 2013 4 different treatments: Sewage Sludge (SS) Green compost Farmyard manure Inorganic fertilizer Treated rate: 2/a, Spring&Autumn Replicates: 4 Plots: 16 (each plot: 3 m×3 m) Sampling rate: Week 0, 2, 4, Month 2, 4, 6 and then every 6 months. Monitoring Contents: Pollutants in water, soils, herbage and earthworms (EDCs and metals) Invertebrate population (nematode) Herbage height Soil Organic Matter
Long-term BOFs Amended Soils Experiment
Acknowledgment
Carol KYLE Rupert HOUGH
Morgane LE VELLY Elizabeth DUFF
Stewart RHIND Helen RUFFIE
Craig MCKENZIE Emma CALMETTES
Mark OSPREY Dave HAMILTON
Scottish Government’s Rural and Environment Science and
Analytical Services (RESAS) Division
Thank You!