1
GLOBAL SYMPOSIUM ON SOIL POLLUTION 2 - 4 MAY 2018 | FAO - ROME, ITALY Uranium, a new villain among the dirty dozen in soil protection Ewald Schnug 1 , Silvia Haneklaus 1 , Miyuki Maekawa 1 , Yajie Sun 2 , Roland Bol 21 Institute for Crop and Soil Science, Julius Kühn-Institute, Germany 2 Institute of Bio- and Geosciences, IBG -3 : Agrosphere, Forschungszentrum Jülich, Germany INTRODUCTION Agriculture is a main contributor to environmental loads of nearly all elements of the periodic sys- tem, for instance by applying waste-based fertilizer materials such as sewage sludge, and miner- al fertilizers. Particularly mineral P fertilizers contain significant amounts of elements which affect the quality of the environment and food plants. The Institute for Crop and Soil Science of the Julius Kühn-Insti- tute (JKI) estimates annual aver- age loads of some trace elements such as As, Cu, Pb and Zn to agri- cultural land in Germany exclu- sively through the application of P- fertilizers for the time span from 1950/51 to 2016/17 (Table 2). U is not only radioactive but also toxic. The chemical toxicity of U is estimated to be substantially high- er than the radiological hazard. 0 20 40 60 80 100 120 Austria Belguim Bulgaria Croatia Cyprus Czech Republic Denmark Estonia Finland France Germany Greece Hungary Italy Ireland Latvia Luxembourg Lithuania Malta Netherlands Poland Portugal Romania Spain Slovakia Slovenia Sweden United Kingdom 8 10 19 19 1 11 8 2 13 117 71 24 16 63 20 4 0,5 20 0,03 9 97 15 28 116 5 3 8 56 Yearly Uranium Inputs [t] Table 2: Annual average loads of the Elements from 1950/51 to 2016/17 Element As B Cu Ni Mo Pb U Zn [t · a –1 ] 38 1575 170 71 50 14 167 604 Table 1: Evidence for fertilizer-derived U in groundwater - U and nitrate concentrations in neighboring shallow (7–9m) and deep (70–90 m) wells of two waterworks in southern Germany (data from 2008). Location Well Type U [µg · L 1 ] NO 3 [mg · L 1 ] Straubing Shallow 2.8 40 Deep <0.2 2.8 Rehlingen Shallow 10 22 Deep 1.6 8.2 The chemical toxicity of U ranges between that of Hg and Ni, and it is enhanced synergistically by Cd. MAIN RESULTS Soil and drinking water resources pollution with U derived from mineral P-fer- tilizer According to the amount of P 2 O 5 consumption data provided by FAO, about 707 tons U per year are added to agricultural soils in European countries through the application of mineral P-fertilizers (Figure 1). The mean transfer factor for U in soils to crop plants is 0.05 and thus comparable to that of As, Co, Hg and Pb. The by far greatest contri- bution to the daily intake of U by humans has U in drinking water. Fertilizer-derived U is a primary a risk for the quality of groundwa- ter and drinking water (Table 1). At an annual application rate of 9 g·ha –1 U applied with 22 kg·ha –1 P a steady state concentration of 22 μg · L –1 U is expected in the per- colating water. Uranium – the hidden trea- sure in rock phosphates The U in rock phosphates has a high commercial value in context of increasing electricity demand. As in Table 1 shown, 167 t U were spend with mineral P-fertilizers on an average in Germany alone every year. 167 t U contain enough energy to supply 2,350,000 aver- age sized German households and equals the energy of firewood har- vested from 5,600,000 ha forest. From 10 g U (corresponding to a P-fertilization of 22 kg · ha –1 P according to GAP) 500 kW of ener- gy can be produced. Compared to the same amount of energy derived from coal this saves a total of 500 kg CO 2 . CONCLUSION Proposed action to protect soils and water bodies from fertiliz- er-derived uranium Retrieval of U from mineral P- fer- tilizers protects not only soils and waters from this toxic element, but is also an unconventional contri- bution of agriculture to climate protection. In recent years new processes for the extraction of U from rock phosphate or phosphor- ic acid have also been improved . Because of increasing demand and decreasing supply stock market pric- es for U can be expected to be increasing. This implies that invest- ments in technology for the extraction of U from rock phosphates will not yield higher fertilizer prices. Figure 1: Estimated annual U input to agricultural soils with mineral P fertilizers in the European Union (based on FAO data 2002-2013)

Uranium, a new villain among the dirty dozen in soil protectionUranium, a new villain among the dirty dozen in soil protection Ewald Schnug1, Silvia Haneklaus1, Miyuki Maekawa1, Yajie

  • Upload
    others

  • View
    2

  • Download
    0

Embed Size (px)

Citation preview

Page 1: Uranium, a new villain among the dirty dozen in soil protectionUranium, a new villain among the dirty dozen in soil protection Ewald Schnug1, Silvia Haneklaus1, Miyuki Maekawa1, Yajie

G L O B A L S Y M P O S I U MO N S O I L

P O L L U T I O N2 - 4 M A Y 2 0 1 8 | F A O - R O M E , I T A L Y

Uranium, a new villain among the dirty dozen in soil protection

Ewald Schnug1, Silvia Haneklaus1, Miyuki Maekawa1, Yajie Sun2, Roland Bol21

Institute for Crop and Soil Science, Julius Kühn-Institute, Germany2Institute of Bio- and Geosciences, IBG-3: Agrosphere, Forschungszentrum Jülich, Germany

INTRODUCTION

Agriculture is a main contributor to environmental loads of nearly all elements of the periodic sys-tem, for instance by applying waste-based fertilizer materials such as sewage sludge, and miner-al fertilizers. Particularly mineral P fertilizers contain significant amounts of elements which affect the quality of the environment and food plants.The Institute for Crop and Soil Science of the Julius Kühn-Insti-tute (JKI) estimates annual aver-age loads of some trace elements such as As, Cu, Pb and Zn to agri-cultural land in Germany exclu-sively through the application of P- fertilizers for the time span from 1950/51 to 2016/17 (Table 2). U is not only radioactive but also toxic. The chemical toxicity of U is estimated to be substantially high-er than the radiological hazard.

0

20

40

60

80

100

120

Austr

ia

Belgu

im

Bulga

ria

Croa

tia

Cypr

us

Czec

h Re

publi

c

Denmar

k

Esto

nia

Finlan

d

Fran

ce

German

y

Greec

e

Hunga

ryIta

ly

Irelan

d

Latv

ia

Luxe

mbo

urg

Lithu

ania

Malta

Neth

erlan

ds

Polan

d

Portu

gal

Roman

iaSp

ain

Slova

kia

Slove

nia

Swed

en

Unite

d King

dom

8 10

19 19

1

11 82

13

117

71

24

16

63

20

40,5

20

0,03

9

97

15

28

116

5 38

56

Year

ly U

rani

um I

nput

s [t

]

Table 2: Annual average loads of the Elements from 1950/51 to 2016/17

Element As B Cu Ni Mo Pb U Zn[t · a–1 ] 38 1575 170 71 50 14 167 604

Table 1: Evidence for fertilizer-derived U in groundwater - Uand nitrate concentrations in neighboring shallow (7–9m)and deep (70–90 m) wells of two waterworks in southern Germany (data from 2008).

Location Well Type U [µg · L–1] NO3 [mg · L–1]Straubing Shallow 2.8 40

Deep <0.2 2.8Rehlingen Shallow 10 22

Deep 1.6 8.2

The chemical toxicity of U ranges between that of Hg and Ni, and it is enhanced synergistically by Cd.

MAIN RESULTS

Soil and drinking water resources pollution with U derived from mineral P-fer-tilizerAccording to the amount of P2O5 consumption data provided by FAO, about 707 tons U per year are added to agricultural soils in European countries through the application of mineral P-fertilizers (Figure 1). The mean transfer factor for U in soils to crop plants is 0.05 and thus comparable to that of As, Co, Hg and Pb. The by far greatest contri-bution to the daily intake of U by humans has U in drinking water. Fertilizer-derived U is a primary a risk for the quality of groundwa-ter and drinking water (Table 1).

At an annual application rate of 9 g·ha–1 U applied with 22 kg·ha–1 P a steady state concentration of 22 µg · L–1 U is expected in the per-colating water.

Uranium – the hidden trea-sure in rock phosphatesThe U in rock phosphates has a high commercial value in context of increasing electricity demand. As in Table 1 shown, 167 t U were spend with mineral P-fertilizers on an average in Germany alone every year. 167 t U contain enough energy to supply 2,350,000 aver-age sized German households and equals the energy of firewood har-vested from 5,600,000 ha forest. From 10 g U (corresponding to a P-fertilization of 22 kg · ha–1 P according to GAP) 500 kW of ener-gy can be produced. Compared to the same amount of energy derived from coal this saves a total of 500 kg CO2.

CONCLUSION

Proposed action to protect soils and water bodies from fertiliz-er-derived uraniumRetrieval of U from mineral P- fer-tilizers protects not only soils and waters from this toxic element, but is also an unconventional contri-bution of agriculture to climate protection. In recent years new processes for the extraction of U from rock phosphate or phosphor-ic acid have also been improved .Because of increasing demand and decreasing supply stock market pric-es for U can be expected to be increasing. This implies that invest-ments in technology for the extraction of U from rock phosphates will not yield higher fertilizer prices.

Figure 1: Estimated annual U input to agricultural soils with mineral P fertilizers in the European Union (based on FAO data 2002-2013)