Design

Our motivation is to solve large area soil contamination using plant-endophyte synergism. We combine phytoremediation and our engineered endophyte together to clean dioxin in soil. Two of our genes are derived from the transcriptomic data of Burkholderia cenocepacia 869T2 under dioxin-containing condition.

Genes

TonB

TonB-dependent receptors are membrane bound proteins of Gram-negative bacteria that can actively transport the ferric ion carrier, siderophore, which is similar in structure with dioxin^[3].

Researches have shown that, some macromolecule such as carbonhydrate, heme or vitamin B12 can permeate TonB-dependent receptor^[1,6].

Our TonB protein is derived from transcriptomic data under dioxin-stressed condition of Burkholderia cenocepacia 869T2. It is up-regulated during early growth period (pre-log phase)^[2,13]. It can be also found in famous dioxin degradable bacteria, Sphingomonas wittichii RW1^[9].

The docking results have shown that the protein structure can allow the passage of TCDD and some other dioxin compound.

HAD

Haloacid dehalogenases (HAD) are a family of bacterial enzymes. Generally, most of HAD superfamily members catalyze the dephosphorylation of various compounds, but the catalyzation of carbon group transfer is unique. (Burroughs et al., 2006) 2-haloacid dehalogenase, which we used in our project, is a representative of haloacid dehalogenase (HAD) superfamily, that can catalyze the cleavage of carbon-halogen bonds of halogenated compounds, which are produced worldwide in a large amount of served human usages as solvents, synthetic precursors, agrochemicals, etc. (Kurihara, 2011). The catalyzation by 2-HAD needs without a metal ion cofactor while other HAD enzymes need, and that a water nucleophile attacks the Asp C=O in the hydrolysis partial reaction (Burroughs et al., 2006).

2-HADs are classified into three kinds based on substrate specificities, including L-2-haloacid dehalogenase, D-2-haloacid dehalogenase and DL-2-haloacid dehalogenase. (Kurihara et al., 2000). There are two reaction mechanisms proposed for L-2-haloacid dehalogenase. For the first reaction mechanism in Fig. N-A, a carboxylate group of the enzyme attacks the α-carbon atom of the substrate to release the halogen atom to form an ester intermediate. After that, the ester intermediate is hydrolyzed to produce D-2-hydroxyalkanoic acid and regenerate the enzyme. As for the second mechanism, a water molecule directly attacks the substrate to expel the halogen atom in the single step in Fig. 5- B (Kurihara et al., 2000).

Since numerous haloacid dehalogenases isolated from various bacteria species, the potential of bacteria using HAD to do bioremediation and utilize these compounds as its carbon source increases.

Laccase

The laccase we adopt in this system is from a symbiotic fungus of termite ( Odontotermes formosanus), Termitomyces T984, which was isolated from fecal material and responsible for lignin degradation where laccase plays a crucial role.

The laccase are a kind of peroxidase that has great oxidation ability and has potential to degrade organic compound such as diesel, pesticide, antibiotics, PCBs, dioxins etc. In former research, the laccase we use has shown

which can attack the ring structure on the dioxin and turn it into some products that can enter lower metabolic pathway of bacteria. (Mathew2013, Jiang2016, Zhang2012)

Circuit

We use constitutive Anderson promoter J23100 and strong RBS B0034 to express our genes as a polygene (polycistronic) circuit. Since the total length of our genes is short enough (less than 5000) we can express it right away.

Shuttle vectors

To express our genes in endophyte, we found some broad host range shuttle vector and get it from addgene.

We decided to replace the ori from pSB1C3 with the replication-related proteins and ori on the shuttle vectors. After we searched for the restriction sites, we decide to add BamHI and HindIII by PCR on the shuttle vectors and pSB1C3, then, digest it and ligate it (Figure n).

pME6010 is a small, stable, high copy number (n = 5.9 ± 1.8) shuttle vector based on the minimal pVS1 replicon for use in gram-negative especially plant-associated bacteria with tetracycline resistance. The vector we used was originally from Dr. Herman Spaink’s Lab, Leiden University. We bought it from addgene as the name, pMP4657, which contains pLacZ-EGFP (stuurman2000).

pBBR1

pBBR1 is relatively small( <5.3kb), and they possess an extended multiple cloning site (MCS). They have the LacZα peptide that allow direct selection of recombinant plasmid in Escherichia coli. Moreover, pBBR1 provide four different antibiotics including kanamycin, ampicillin, tetracycline, gentamycin. This let pBBR1 broaden it usage. The plasmids have been tested and found to replicate in Pseudomonas fluorescens.(kovach1995) According Burkholderia genus and Pseudomonas fluorescens are close, pBBR1 can express in Burkholderia genus.

Template	Primers
pSB1C3 or pSB series plasmid backbone	BBaddBam F CGCGGATCCGCGcgaaaactcacgttaagg BBaddHin R CCCAAGCTTGGGgtattaccgcctttgag tr
pMP4657 (pME6010 with GFP)	V4657addBamF CGCGGATCCgcggctgcatgaaatcct V4657addHinR CCCAAGCTTgggtgtcagtgaagtgct
pBBR1MCS	BBRaddBamF CGCGGATCCgcgccatcagatccttg BBRaddBamF2 CGCGGATCCgcgggccactcaatgctt BBRaddHinR CCCAAGCTTgggcagggtcgttaaatag

Experimental Plan

Reference

1. Blanvillain, Servane, Meyer, Damien, Boulanger, Alice, Lautier, Martine, Guynet, Catherine, Denancé, Nicolas, . . . Arlat, Matthieu. (2007). Plant carbohydrate scavenging through TonB-dependent receptors: a feature shared by phytopathogenic and aquatic bacteria. PLoS one, 2(2), e224.
2. Chang, Kung-Hao. (2016). To study the change in transcriptome of Burkholderia cenocepacia 869T2, when exposed to dioxin, and to predict the relationship between TonB-dependent siderophore receptor and dioxin. Master Thesis from the National Chung Hsing University.
3. Chimento, David P, Kadner, Robert J, & Wiener, Michael C. (2003). The Escherichia coli outer membrane cobalamin transporter BtuB: structural analysis of calcium and substrate binding, and identification of orthologous transporters by sequence/structure conservation. Journal of molecular biology, 332(5), 999-1014.
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5. Jiang, Yu-Han. (2016).The possibility of the degradation of dioxin with recombinant Laccase protein from Odontotermes formosanus symbiosis strain Termitomyces T984. Master Thesis from the National Chung Hsing University.
6. Kai Tang, Nianzhi Jiao, Keshao Liu, Yao Zhang and Shuhui Li. (2012). Distribution and Functions of TonB-Dependent Transporters in Marine Bacteria and Environments: Implications for Dissolved Organic Matter Utilization. PLoS ONE, 7(7).
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9. Miller, T. R., Delcher, A. L., Salzberg, S. L., Saunders, E., Detter, J. C., & Halden, R. U. (2010). Genome sequence of the dioxin-mineralizing bacterium Sphingomonas wittichii RW1. Journal of bacteriology, 192(22), 6101-6102.
10. Neilands, J. B. (1995). Siderophores: structure and function of microbial iron transport compounds. Journal of Biological Chemistry, 270(45), 26723-26726.
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15. Burroughs, A. M., Allen, K. N., Dunaway-Mariano, D., & Aravind, L. (2006). Evolutionary genomics of the HAD superfamily: understanding the structural adaptations and catalytic diversity in a superfamily of phosphoesterases and allied enzymes. Journal of molecular biology, 361(5), 1003-1034.
16. Kurihara, T. (2011). A mechanistic analysis of enzymatic degradation of organohalogen compounds. Bioscience, biotechnology, and biochemistry, 75(2), 189-198.
17. Kurihara, T., Esaki, N., & Soda, K. (2000). Bacterial 2-haloacid dehalogenases: structures and reaction mechanisms. Journal of Molecular Catalysis B: Enzymatic, 10(1-3), 57-65.